Air Quality Criteria for Lead Volume II of II - (NEPIS)(EPA) - US ...

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AX5-135 Table AX5-8.3 (cont’d). Bone Cell Cultures Utilized to Test Effects of Lead Compound Dose/Concentration Duration Exposure Route Species Effects Blood Level Reference Pb acetate 0.1 to 30 µM 24 h In medium Abbreviations Chicken growth plate and sternal chondrocytes Pb—lead µCi—microCurie IU—international units hr—hour OB—osteoblast 5F-BAPTA—1,2-bis(2-amino-5-fluorophenoxy)ethane-N,N,N’,N’-tetraacetic acid [Pb 2+ ]i—free intracellular lead FURA-2—1-[6-Amino-2-(5-carboxy-2-oxazolyl)-5-benzofuranyloxy]-2-(2-amino-5methylphenoxy) ethane-N,N,N',N'-tetraacetic acid M—molar DNA—deoxyribonucleic acid ∆M—decrease in magnetization of intracellular Pi upon prolonged saturation of gammaphosphate of ATP mM—millimolar Kcat—activation constant IC50—inhibitory concentration 50% mg—milligram 210 Pb—lead-210 radionuclide EM—experimental medium mU—milliunits 45 Ca—calcium-45 radionuclide CRAC—calcium release activated calcium reflux pg—picogram mRNA—messenger ribonucleic acid ng—nanogram A dose-dependent inhibition of thymidine incorporation into growth plate chondrocytes was found with exposure to 1–30 µM Pb for 24 h. A maximal 60% reduction occurred at 30 µM. Pb blunted the stimulatory effects on thymidine incorporation produced by TGF-β1 (24% reduction) and PTHrP (19% reduction), however, this effect was less than with Pb alone. Pb (1 and 10 µM) increased type X collagen in growth plate chondrocytes ~5.0-fold and 6.0-fold in TGF-β1 treated cultures and 4.2-fold and 5.1-fold in PTHrP treated cultures when compared with controls, respectively. Pb exposure alone reduced type X collagen expression by 70–80%. Vmax—maximum velocity TGF-β1—transforming growth factor-beta 1 mL—milliliter i.v.—intravenous CM—control medium µM—micromolar ng—nanogram [Ca 2+ ]i —free intracellular calcium PGE2—prostaglandin E2 PKC—protein kinase C Kd—dissociation constant nmol—nanomole HOS TE 85 cells—human osteosarcoma cells PTHrP—parathyroid hormone-related protein GD—gestational day PTH—parathyroid hormone min—minute OC—osteoclast ROS 17/2.8—rat osteosarcoma cells nM—nanomolar h—hour IGF-I—insulin growth factor I ATP—adenosine triphosphate EGF—epidermal growth factor Not applicable Zuscik et al. (2002)
AX5-136 Table AX5-8.4. Bone Lead as a Potential Source of Toxicity in Altered Metabolic Conditions Compound Dose/Concentration Duration Exposure Route Species Effects Blood Level Reference Pb acetate 200 µg/mL 105 days prior to mating or 105 days prior to mating and during gestation and lactation (160 days) In drinking water Pb acetate 12 mM 8 wks prior to mating and during gestation In drinking water Pb acetate 100 ppm (A) Exposure for 158 ± 2 days from 21 days of age to midlactation; (B) Exposure 144 ± 2 days from day 21 up to delivery; (C) Exposure only during lactation; (D, E, and F) groups of nonpregnant rats exposed for periods equivalent to groups A, B and C, respectively. In drinking water Mice Results suggested very little Pb was transferred from mother to fetus during gestation, however, Pb transferred in milk and retained by the pups accounted for 3% of the maternal body burden of those mice exposed to Pb prior to mating only. The amount of Pb retained in these pups exceeded that retained in the mothers, suggesting lactation effectively transfers Pb burden from mother to suckling offspring. Transfer of Pb from mothers was significantly higher when Pb was supplied continuously in drinking water, rather than terminated prior to mating. Rat Considerably higher lactational transfer of Pb from rat dams compared to placental transfer was reported. Continuous exposure of rat dams to Pb until day 15 of lactation resulted in milk Pb levels 2.5 times higher than in whole blood, while termination of maternal Pb exposure at parturition yielded equivalent blood and milk levels of Pb, principally from Pb mobilized from maternal bone. Rat In rats exposed to Pb 144 days prior to lactation (B), the process of lactation itself elevated blood Pb and decreased bone Pb, indicating mobilization of Pb from bone as there was no external source of Pb during the lactation process. Rats exposed to Pb for 158 days (A)(144 days prior to lactation and 14 days during lactation) also experienced elevated blood Pb levels and loss of Pb from bone. Pb exposure only during the 14 days of lactation was found to significantly increase intestinal absorption and deposition (17 fold increase) of Pb into bone compared to nonpregnant rats, suggesting enhanced absorption of Pb takes place during lactation. The highest concentration of Pb in bone was found in nonpregnant, nonlactating control animals, with significantly decreased bone Pb in lactating rats secondary to bone mobilization and transfer via milk to suckling offspring. Not given Keller and Doherty (1980) Concentration (µg/l) in whole blood at day 15 of lactation: Controls = 14 ± 4; Pbexposed until parturition = 320 ± 55; Pb-exposed until day 15 of lactation = 1260 ± 171* *p < 0.001 compared with dams at parturition. Concentration (µg/dL) in whole blood at day 14 of lactation or equivalent: Group A = 31.2 ± 1.1; Group B = 28.0 ± 1.7; Group D = 27.3 ± 2.2; Group E = 24.7 ± 1.2 Palminger Hallén et al. (1996) Maldonado-Vega et al. (1996)
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October 2006 EPA/600/R-05/144bF Air
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PREFACE National Ambient Air Qualit
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NCEA acknowledges the valuable cont
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Table of Contents Page PREFACE ....
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Authors, Contributors, and Reviewer
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Contributors and Reviewers (cont’
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Contributors and Reviewers (cont’
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Executive Direction U.S. Environmen
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Chair U.S. Environmental Protection
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Abbreviations and Acronyms αFGF α
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BLL blood lead level BLM biotic lig
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CRI chronic renal insufficiency CSF
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EPT macroinvertebrates from the Eph
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GRP78 glucose-regulated protein 78
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KABC Kaufman Assessment Battery for
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NADP nicotinamide adenine dinucleot
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Pb(Ac)2 lead acetate PbB blood lead
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RR RT RSEM RSUC RT ∑SEM SA7 SAB S
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TGF transforming growth factor TH t
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AX4. CHAPTER 4 ANNEX ANNEX TABLES A
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AX4-3 Table AX4-1 (cont’d). Analy
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AX4-5 Table AX4-2 (cont’d). Summa
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AX4-7 Table AX4-3. Bone Lead Measur
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AX4-9 Reference, Study Location, an
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AX4-11 Table AX4-4 (cont’d). Bone
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AX4-19 Reference, Study Location, a
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AX4-37 Table AX4-9 (cont’d). Lead
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AX4-39 Table AX4-11. Summary of Sel
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AX4-41 Table AX4-11 (cont’d). Sum
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AX-43 Table AX4-12 (cont’d). Summ
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Barltrop, D.; Meek, F. (1979) Effec
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Carroll, R. J.; Galindo, C. D. (199
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Flegal, A. R.; Smith, D. R. (1995)
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Gulson, B.; Mizon, K.; Smith, H.; E
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Khoury, G. A.; Diamond, G. L. (2003
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Morgan, W. D.; Ryde, S. J.; Jones,
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Pounds, J. G.; Leggett, R. W. (1998
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Skerfving, S. (1988) Biological mon
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U.S. Environmental Protection Agenc
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Air Quality Criteria for Lead Volum
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AQCD/Addendum and 1990 Supplement,
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Air Quality Criteria for Lead (Seco
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List of Tables AX4-1 Analytical Met
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List of Tables (cont’d) AX5-6.3 G
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List of Tables (cont’d) AX5-9.3 S
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Principal Authors (cont’d) Author
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Principal Authors Authors, Contribu
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Principle Authors (cont’d) Author
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Technical Support Staff U.S. Enviro
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Members (cont’d) U.S. Environment
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ANP atrial natriuretic peptide AP a
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CCE Coordination Center for Effects
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DR drinking water DSA delayed spati
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FTII Fagan Test of Infant Intellige
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H3PO4 phosphoric acid HPRT hypoxant
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MATC maximum acceptable threshold c
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NOS nitric oxide synthase; not othe
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PPVT-R Peabody Picture Vocabulary T
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SOPR sperm-oocyte penetration rate
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vit C vitamin C vit E vitamin E VMA
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AX5-2 Table AX5-2.1. Effect of Lead
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AX5-4 Table AX5-2.1 (cont’d). Eff
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AX5-6 Table AX5-2.2. Lead, Erythroc
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AX5-8 Table AX5-2.2 (cont’d). Lea
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AX5-10 Table AX5-2.4. Lead Effects
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AX5-12 Table AX5-2.5. Lead Interact
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AX5-14 Table AX5-2.7. Lead, Erythro
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AX5-16 Subject Exposure Protocol Ra
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AX5-22 Subject Rat, female, 22 wks
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AX5-24 Subject Rat, F344, male Expo
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AX5-26 Subject Monkey, cynomolgus,
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AX5-28 Subject Rat, SD, male, PND 6
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AX5-30 Subject Monkey, cynomolgus,
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AX5-32 Subject Exposure Protocol Ta
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AX5-34 Table AX5-3.6 (cont’d). Ke
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AX5-36 Table AX5-3.6 (cont’d). Ke
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AX5-38 Citation Al-Hakkak et al. (1
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AX5-40 Citation Fox et al. (1997)
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AX5-42 Citation Pinon- Lataillade e
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AX5-44 Citation Wiebe et al. (1998)
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AX5-46 Citation Chowdhuri et al. (2
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AX5-48 Citation Graca et al. (2004)
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AX5-50 Citation Marchlewicz et al.
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AX5-52 Table AX5-4.2 (cont’d). Ef
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AX5-54 Citation Sokol et al. (1985)
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AX5-56 Citation Table AX5-4.3 (cont
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AX5-58 Citation Priya et al. (2004)
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ANNEX TABLES AX5-5 AX5-60
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AX5-62 Table AX5-5.1 (cont’d). In
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AX5-64 Table AX5-5.1 (cont’d). In
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AX5-66 Reference Watts et al. (1995
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AX5-68 Reference Lai et al. (2002)
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AX5-70 Reference Shelkovnikov and G
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AX5-72 Reference Fujiwara and Kaji
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AX5-74 Reference Fugiwara et al. (1
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AX5-76 Table AX5-6.1. Genotoxic/Car
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AX5-78 Table AX5-6.2. Genotoxic/Car
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AX5-80 Table AX5-6.3 (cont’d). Ge
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AX5-82 Table AX5-6.4 (cont’d). Ge
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Page 227 and 228: AX5-86 Compound Table AX5-6.6. Geno
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Page 237 and 238: AX5-96 Table AX5-6.10 (cont’d). G
Page 239 and 240: AX5-98 Table AX5-6.12. Genotoxic/Ca
Page 241 and 242: AX5-100 Table AX5-6.14. Genotoxic/C
Page 243 and 244: AX5-102 Compound Table AX5-6.16. Ge
Page 245 and 246: AX5-104 Table AX5-6.18. Genotoxic/C
Page 247 and 248: AX5-106 Table AX5-6.18 (cont’d).
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Page 263 and 264: AX5-122 Table AX5-8.1. Bone Growth
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Page 289 and 290: AX5-148 Nature of Exposure Table AX
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Page 297 and 298: ANNEX TABLES AX5-10 AX5-156
Page 303 and 304: AX5-162 Table AX5-10.2. Biochemical
Page 307 and 308: AX5-166 Table AX5-10.4. Lead, Oxida
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Page 325 and 326: AX5-184 Table AX5-10.9. Lead, Calci
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AX5-188 Source Organ Species Table
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REFERENCES Abdollahi, M.; Dehpour,
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Bataineh, H.; Al-Hamood, M. H.; Elb
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Buchet, J.-P.; Roels, H. E.; Huberm
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Cline, H. T.; Witte, S.; Jones, K.
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Cory-Slechta, D. A.; McCoy, L.; Ric
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children's health: immune and respi
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Ferguson, C.; Kern, M.; Audesirk, G
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Fullmer, C. S. (1991) Intestinal ca
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Goyer, R. A.; Leonard, D. L.; Moore
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Hengstler, J. G.; Bolm-Audorff, U.;
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Jacquet, P.; Leonard, A.; Gerber, G
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Kim, K. A.; Chakraborti, T.; Goldst
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Laughlin, N. K.; Bowman, R. E.; Fra
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Maldonado-Vega, M.; Cerbón-Solórz
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Moorman, W. J.; Skaggs, S. R.; Clar
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O'Flaherty, E. J.; Inskip, M. J.; F
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Price, R. G.; Taylor, S. A.; Chiver
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Rodamilans, M.; Mtz.-Osaba, M. J.;
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Schlipkoter, H.-W.; Frieler, L. (19
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Skoczyńska, A.; Smolik, R.; Jeleń
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Tavakoli-Nezhad, M.; Pitts, D. K. (
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Valentino, M.; Governa, M.; Marchis
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Wetmur, J. G.; Lehnert, G.; Desnick
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Zhou, J.; Xu, Y.-H.; Chang, H.-F. (
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Air Quality Criteria for Lead Volum
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The purpose of this revised Lead AQ
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Air Quality Criteria for Lead (Seco
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List of Tables Number Page AX6-2.1
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List of Tables (cont’d) Number Pa
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ANOVA analysis of variance ANP atri
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CCD charge-coupled device CCE Coord
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DPPD N-N-diphenyl-p-phynylene-diami
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FTES free testosterone FTII Fagan T
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HPLC high-pressure liquid chromatog
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MAO monoamine oxidase MATC maximum
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NORs nucleolar organizing regions N
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ppm parts per million PPVT-R Peabod
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AX6-4 Table AX6-2.1 (cont’d). Pro
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AX6-10 Table AX6-2.2 (cont’d). Me
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AX6-12 Table AX6-2.3 (cont’d). Cr
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AX6-14 Table AX6-2.4. Effects of Le
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AX6-24 Table AX6-2.8. Effects of Le
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AX6-28 Table AX6-2.10 (cont’d). R
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AX6-30 Table AX6-3.1. Neurobehavior
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AX6-32 Table AX6-3.1 (cont’d). Ne
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AX6-34 Table AX6-3.2 (cont’d). Sy
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AX6-36 Table AX6-3.3. Neurobehavior
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AX6-50 Table AX6-3.4 (cont’d). Me
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AX6-56 Table AX6-3.6. Evoked Potent
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AX6-58 Table AX6-3.6 (cont’d). Ev
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AX6-60 Table AX6-3.7 (cont’d). Po
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AX6-62 Table AX6-3.7 (cont’d). Po
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AX6-64 Table AX6-3.8 (cont’d). Oc
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AX6-66 Table AX6-3.9. Other Neurolo
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AX6-68 Table AX6-3.9 (cont’d). Ot
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AX6-70 Table AX6-4.1. Renal Effects
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AX6-72 Table AX6-4.1 (cont’d). Re
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AX6-104 Table AX6-4.3. Renal Effect
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AX6-130 Table AX6-5.1. Effects of L
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AX6-132 Table AX6-5.1 (cont’d). E
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AX6-166 Table AX6-5.4. Cardiovascul
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AX6-170 Table AX6-6.1 (cont’d). P
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AX172 Table AX6-6.1 (cont’d). Pla
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AX6-174 Table AX6-6.2. Lead Exposur
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AX6-176 Table AX6-6.2 (cont’d). L
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AX6-186 Table AX6-7.2. Key Occupati
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AX6-188 Table AX6-7.2 (cont’d). K
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AX6-190 Table AX6-7.2 (cont’d). K
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AX6-192 Table AX6-7.3. Key Studies
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AX6-194 Table AX6-7.4. Other Studie
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AX6-196 Table AX6-7.4 (cont’d). O
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AX6-224 Table 6-9.2 (cont’d). Eff
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AX6-232 Table AX6-9.3 (cont’d.).
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AX6-258 Table AX6-9.10. Effects of
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REFERENCES Abbate, C.; Buceti, R.;
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Baghurst, P. A.; McMichael, A. J.;
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Bolla, K. I.; Schwartz, B. S.; Stew
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Chia, K. S.; Jeyaratnam, J.; Tan, C
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David, O. J.; Clark, J.; Hoffman, S
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Englyst, V.; Lundstrom, N. G.; Gerh
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Gennart, J. P.; Bernard, A.; Lauwer
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Haraguchi, T.; Ishizu, H.; Takehisa
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Jemal, A.; Graubard, B. I.; Devesa,
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Lanphear, B. P.; Howard, C.; Eberly
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Lundström, N.-G.; Nordberg, G.; En
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Muntner, P.; He, J.; Vupputuri, S.;
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Paksy, K.; Gáti, I.; Náray, M.; R
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Rhainds, M.; Levallois, P.; Dewaill
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Sargent, J. D.; Dalton, M. A.; O'Co
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Sheffet, A.; Thind, I.; Miller, A.
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Stevens, L. A.; Levey, A. S. (2005b
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Van Larebeke, N.; Koppen, G.; Nelen
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Winker, R.; Ponocny-Seliger, E.; R
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October 2006 EPA/600/R-05/144bF Air
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PREFACE National Ambient Air Qualit
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drafts of document materials were r
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Table of Contents PREFACE..........
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Table of Contents (cont’d) II-ix
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List of Tables (cont’d) AX7-2.3.1
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List of Figures (cont’d) Number P
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ANOVA analysis of variance ANP atri
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CCD charge-coupled device CCE Coord
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DPPD N-N-diphenyl-p-phynylene-diami
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FTES free testosterone FTII Fagan T
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HPLC high-pressure liquid chromatog
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MAO monoamine oxidase MATC maximum
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NORs nucleolar organizing regions N
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ppm parts per million PPVT-R Peabod
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Pb is ideally suited for this task.
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Concept For a given metal or metall
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(1979) observed that “the smaller
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Figure AX7-1.1.3. Illustration of p
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• Colorimetric • Electrochemica
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Figure AX7-1.1.5. Bulk lead versus
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diffraction lines and comparing the
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The major disadvantage of SIMS to s
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techniques can be useful in a study
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have included phosphoric acid (H3PO
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to 15 years after biosolid applicat
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thin films (DGT), and ICP technique
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completely extract targeted phases.
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epresents Eb. The precise energy re
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1974; Ruby et al., 1994). However,
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T1/2 = 14 × 10 9 year). The result
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floor) time-series data to evaluate
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contributions of dry deposition may
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Compared to their estimated 20th-ce
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thought to enter the plant via the
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soil was not allowed to equilibrate
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Lead concentrations in various tiss
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that the nematode may detoxify Pb v
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plasma levels of uric acid and crea
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effective use of glutathione metabo
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and oats (Avena sativa) had signifi
Page 811 and 812:
other metals is inconsistent (Påhl
Page 813 and 814:
Speciation and Form of Lead Recent
Page 815 and 816:
organism responses to Pb. Section A
Page 817 and 818:
Primary Producers Commonly reported
Page 819 and 820:
solution and minimal translocation
Page 821 and 822:
AX7.1.3.3 Recent Studies on the Eff
Page 823 and 824:
AX7-66 Avian Species Reproduction J
Page 825 and 826:
AX7-68 Avian Species American kestr
Page 827 and 828:
Very little research has been done
Page 829 and 830:
AX7-72 Mammalian Species Reproducti
Page 831 and 832:
AX7-74 Mammalian Species No. of Dos
Page 833 and 834:
Page 835 and 836:
Page 837 and 838:
AX7-80 Mammalia n Species No. of Do
Page 839 and 840:
A literature search and review was
Page 841 and 842:
Table AX7-1.3.6. Invertebrate Toxic
Page 843 and 844:
The effects of Pb-chloride on the p
Page 845 and 846:
Ecological Soil Screening Levels (E
Page 847 and 848:
Since the movement and fate of Pb i
Page 849 and 850:
Land Use and Industry Changes in la
Page 851 and 852:
lakes in the United Kingdom the dis
Page 853 and 854:
zinc; had very low pH; and were det
Page 855 and 856:
Sites Affected by Long-Range Lead T
Page 857 and 858:
iomass carbon. Because of this link
Page 859 and 860:
in an oak woodland site 3 km from a
Page 861 and 862:
the forested Lehstenbach catchment
Page 863 and 864:
there is little evidence that Pb ac
Page 865 and 866:
ecosystems. Just as in the terrestr
Page 867 and 868:
To develop chronic AWQC, acceptable
Page 869 and 870:
for the binding of free-metal ion a
Page 871 and 872:
partition in sediment between acid-
Page 873 and 874:
AX7.2.1.5 Metal Mixtures As discuss
Page 875 and 876:
varies from 4:1 in rural streams to
Page 877 and 878:
Organic compounds in surface waters
Page 879 and 880:
solution phase, complexation with c
Page 881 and 882:
The NAWQA dataset was chosen over o
Page 883 and 884:
Lead Distributions Generated from t
Page 885 and 886:
AX7-128 Figure AX7-2.2.3. Spatial d
Page 887 and 888:
AX7-130 Figure AX7-2.2.5. Spatial d
Page 889 and 890:
AX7-132 ` Figure AX7-2.2.7. Spatial
Page 891 and 892:
Figure AX7-2.2.8. Frequency distrib
Page 893 and 894:
Table AX7-2.2.4. Summary Statistics
Page 895 and 896:
Table AX7-2.2.5. Comparison of NCBP
Page 897 and 898:
AX7-140 Figure AX7-2.2.13. Spatial
Page 899 and 900:
calculations indicate that only a s
Page 901 and 902:
from municipal sewage, storm runoff
Page 903 and 904:
AX7.2.3 Aquatic Species Response/Mo
Page 905 and 906:
aquatic plants and insects and on t
Page 907 and 908:
designed to model uptake, MINTEQ pr
Page 909 and 910:
sequestering to organ tissues). The
Page 911 and 912:
AbdAllah and Moustafa (2002) studie
Page 913 and 914:
Summary of Detoxifiction Processes
Page 915 and 916:
1.1 µg/L Cd, 12 µg/L Cu, 55 µg/L
Page 917 and 918:
Studies have identified ALAD in fis
Page 919 and 920:
metals over nonessential metals. Th
Page 921 and 922:
In summary, relationships between a
Page 923 and 924:
potential toxic effects in other or
Page 925 and 926:
esulted in 91.7% survival (Horne an
Page 927 and 928:
carbon sources (including glucose),
Page 929 and 930:
separate concentration-effects mode
Page 931 and 932:
1994. mSQGQs are useful to risk ass
Page 933 and 934:
Algae The 1986 Lead AQCD (U.S. Envi
Page 935 and 936:
observed in Selenastrum capricornut
Page 937 and 938:
Nitrate uptake reported after 48, 7
Page 939 and 940:
1997). The most sensitive primary p
Page 941 and 942:
Freshwater Invertebrates Acute and
Page 943 and 944:
AX7-186 Amphipod (Hyalella azteca)
Page 945 and 946:
concentrations of
Page 947 and 948:
AX7-190 Freshwater Species Chemical
Page 949 and 950:
AX7-192 Species Chemical Frogs (Ran
Page 951 and 952:
studied using Spirodela polyrhiza,
Page 953 and 954:
However, in other cases multivariat
Page 955 and 956:
species was observed. Similar, sign
Page 957 and 958:
AX7-200 Table AX7-2.5.2. Essential
Page 959 and 960:
AX7-202 Table AX7-2.5.2 (cont’d).
Page 961 and 962:
variables, it does not imply causat
Page 963 and 964:
Poulton et al. (1995), the effects
Page 965 and 966:
metal levels. Furthermore, although
Page 967 and 968:
environment through bioaccumulation
Page 969 and 970:
Angle, C. R.; McIntire, M. S.; Colu
Page 971 and 972:
Black, M. C.; Ferrell, J. R.; Horni
Page 973 and 974:
Clements, W. H. (1994) Benthic inve
Page 975 and 976:
Ekenler, M.; Tabatabai, M. (2002) E
Page 977 and 978:
Getz, L. L.; Haney, A. W.; Larimore
Page 979 and 980:
Houlton, B. Z.; Driscoll, C. T.; Fa
Page 981 and 982:
Krüger, F.; Gröngröft, A. (2003)
Page 983 and 984:
Manceau, A.; Lanson, B.; Schlegel,
Page 985 and 986:
Niyogi, S.; Wood, C. M. (2003) Effe
Page 987 and 988:
Rand, G. M.; Wells, P. G.; McCarty,
Page 989 and 990:
Scherer, E.; McNicol, R. E. (1998)
Page 991 and 992:
Sturges, W. T.; Barrie, L. A. (1987
Page 993 and 994:
U.S. Environmental Protection Agenc
Page 995 and 996:
Zenk, M. H. (1996) Heavy metal deto
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