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AX6-113 Table AX6-4.3 (cont’d). Renal Effects of Lead in the Patient Population Reference, Study Location, and Period Study Description Pb Measurement Findings, Interpretation Asia (cont’d) Lin et al. (2001a) Taiwan Study date not provided 24 mo prospective observational study 110 patients with CRI dichotomized by EDTA chelatable Pb level of 80 µg/72 hrs into two groups of 55 each. Eligibility criteria included serum creatinine from 1.5 – 4.0 mg/dL, stable renal function (decrease in GFR
AX6-114 Table AX6-4.3 (cont’d). Renal Effects of Lead in the Patient Population Reference, Study Location, and Period Study Description Pb Measurement Findings, Interpretation Asia (cont’d) Lin et al. (2001a) (cont’d) 3 mo clinical trial of chelation with 1 yr follow-up At 24 mos, 36 patients whose EDTA chelatable Pb levels were 80 - 600 μg/72 hrs and serum creatinine levels of
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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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AX5-80 Table AX5-6.3 (cont’d). Ge
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AX5-86 Compound Table AX5-6.6. Geno
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AX5-96 Table AX5-6.10 (cont’d). G
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AX5-98 Table AX5-6.12. Genotoxic/Ca
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AX5-100 Table AX5-6.14. Genotoxic/C
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AX5-102 Compound Table AX5-6.16. Ge
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AX5-104 Table AX5-6.18. Genotoxic/C
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AX5-106 Table AX5-6.18 (cont’d).
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AX5-110 Compound Assay (Concentrati
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AX5-112 Table AX5-7.1. Light Micros
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AX5-114 Table AX5-7.2. Lead and Fre
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AX5-116 Table AX5-7.2 (cont’d). L
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AX5-118 Table AX5-7.4. Effect of Ch
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AX5-120 Table AX5-7.5 (cont’d). E
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AX5-122 Table AX5-8.1. Bone Growth
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AX5-124 Table AX5-8.1 (cont’d). B
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AX5-126 Table AX5-8.2. Regulation o
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AX5-128 Table AX5-8.2 (cont’d). R
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AX5-136 Table AX5-8.4. Bone Lead as
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AX5-142 Table AX5-8.5. Uptake of Le
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AX5-144 Table AX5-8.7. Effects of L
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AX5-148 Nature of Exposure Table AX
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AX5-150 Table AX5-9.2. Effect of Le
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AX5-152 Species Strain/Gender Age M
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AX5-162 Table AX5-10.2. Biochemical
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AX5-166 Table AX5-10.4. Lead, Oxida
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AX5-180 Table AX5-10.7. Lead and In
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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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AX6-30 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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Page 481 and 482: AX6-64 Table AX6-3.8 (cont’d). Oc
Page 483 and 484: AX6-66 Table AX6-3.9. Other Neurolo
Page 485 and 486: AX6-68 Table AX6-3.9 (cont’d). Ot
Page 487 and 488: AX6-70 Table AX6-4.1. Renal Effects
Page 489 and 490: AX6-72 Table AX6-4.1 (cont’d). Re
Page 517 and 518: AX6-100 Table AX6-4.2 (cont’d). R
Page 521 and 522: AX6-104 Table AX6-4.3. Renal Effect
Page 529: AX6-112 Table AX6-4.3 (cont’d). R
Page 547 and 548: AX6-130 Table AX6-5.1. Effects of L
Page 549 and 550: 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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AX6-234 Table AX6-9.4. Effects of L
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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,
Page 695 and 696:
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
Page 705 and 706:
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
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other metals is inconsistent (Påhl
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Speciation and Form of Lead Recent
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organism responses to Pb. Section A
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Primary Producers Commonly reported
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solution and minimal translocation
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AX7.1.3.3 Recent Studies on the Eff
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AX7-66 Avian Species Reproduction J
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AX7-68 Avian Species American kestr
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Very little research has been done
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AX7-72 Mammalian Species Reproducti
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AX7-74 Mammalian Species No. of Dos
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AX7-80 Mammalia n Species No. of Do
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A literature search and review was
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Table AX7-1.3.6. Invertebrate Toxic
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The effects of Pb-chloride on the p
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Ecological Soil Screening Levels (E
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Since the movement and fate of Pb i
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Land Use and Industry Changes in la
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lakes in the United Kingdom the dis
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zinc; had very low pH; and were det
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Sites Affected by Long-Range Lead T
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iomass carbon. Because of this link
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in an oak woodland site 3 km from a
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the forested Lehstenbach catchment
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there is little evidence that Pb ac
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ecosystems. Just as in the terrestr
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To develop chronic AWQC, acceptable
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for the binding of free-metal ion a
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partition in sediment between acid-
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AX7.2.1.5 Metal Mixtures As discuss
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varies from 4:1 in rural streams to
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Organic compounds in surface waters
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solution phase, complexation with c
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The NAWQA dataset was chosen over o
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Lead Distributions Generated from t
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AX7-128 Figure AX7-2.2.3. Spatial d
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AX7-130 Figure AX7-2.2.5. Spatial d
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AX7-132 ` Figure AX7-2.2.7. Spatial
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Figure AX7-2.2.8. Frequency distrib
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Table AX7-2.2.4. Summary Statistics
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Table AX7-2.2.5. Comparison of NCBP
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AX7-140 Figure AX7-2.2.13. Spatial
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calculations indicate that only a s
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from municipal sewage, storm runoff
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AX7.2.3 Aquatic Species Response/Mo
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aquatic plants and insects and on t
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designed to model uptake, MINTEQ pr
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sequestering to organ tissues). The
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AbdAllah and Moustafa (2002) studie
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Summary of Detoxifiction Processes
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1.1 µg/L Cd, 12 µg/L Cu, 55 µg/L
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Studies have identified ALAD in fis
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metals over nonessential metals. Th
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In summary, relationships between a
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potential toxic effects in other or
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esulted in 91.7% survival (Horne an
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carbon sources (including glucose),
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separate concentration-effects mode
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1994. mSQGQs are useful to risk ass
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Algae The 1986 Lead AQCD (U.S. Envi
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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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