csefh - Kinder-Umwelt-Gesundheit

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Table 13-2. Confidence in Recommendations for Intake of Home-produced Foods General Assessment Factors Rationale Rating Soundness Adequacy of Approach Minimal (or Defined) Bias Applicability and Utility Exposure Factor of Interest Representativeness Currency Data Collection Period Clarity and Completeness Accessibility Reproducibility Quality Assurance The survey methodology and the approach to data analysis were adequate, but individual intakes were inferred from household consumption data. The sample size was large (approximately 3,000 children). Non-response bias can not be ruled out due to low response rate. Also, some biases may have occurred from using household data to estimate individual intake. The analysis specifically addressed home-produced intake. Data from a nationwide survey, representative of the general U.S. population was used. The data were collected in 1987-1988. Household data were collected over 1 week. The methods used described to analyze the data are described in detail in this handbook; the primary data are accessible through USDA. Sufficient detail on the methods used to analyze the data are presented to allow for the results to be reproduced. Quality assurance of NFCS data was good; quality control of the secondary data was sufficient. Child-Specific Exposure Factors Handbook Chapter 13 - Intake of Home-Produced Foods Medium (Means) Low (Distributions) Low (Means & Short-term distributions) Low (Long-term distributions) Page Child-Specific Exposure Factors Handbook 13-4 September 2008 High
Child-Specific Exposure Factors Handbook Chapter 13 - Intake of Home-Produced Foods Table 13-2. Confidence in Recommendations for Intake of Home-produced Food (continued) General Assessment Factors Rationale Rating Variability and Uncertainty Variability in Population Uncertainty Evaluation and Review Peer Review Number and Agreement of Studies Full distributions of home-produced intake rates were provided. Sources of uncertainty include: individuals’ estimates of food weights, allocation of household food to family members, and potential changes in eating patterns since these data were collected, The study was reviewed by USDA and U.S. EPA. The number of studies is 1. Low to Medium Medium Overall Rating Low-Medium (means and short-term distributions) Low (long-term distributions) Child-Specific Exposure Factors Handbook Page September 2008 13-5
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National Center for Environmental A
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CSEFH TABLE OF CONTENTS Child-Speci
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CSEFH 5 TABLE OF CONTENTS (Continue
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CSEFH TABLE OF CONTENTS (Continued)
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CSEFH TABLE OF CONTENTS (Continued)
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CSEFH 16 TABLE OF CONTENTS (Continu
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CSEFH LIST OF TABLES Child-Specific
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CSEFH LIST OF TABLES (Continued) Ch
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CSEFH ACRONYMS AND ABBREVIATIONS Ch
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CSEFH OPP = Office of Pesticide Pro
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CSEFH EXECUTIVE SUMMARY This Child-
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CSEFH were discussed in the guideli
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CSEFH Table ES-1. Summary of Recomm
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CSEFH Youngmoo Kim, U.S. EPA, Regio
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Child-Specific Exposure Factors Han
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exposure assessor) to distinguish b
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is perhaps the most common method o
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uncertainty is high, a sensitivity
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Peretz, C.; Goldberg, P.; Kahan, E.
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Table 2-3. Approaches to Quantitati
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water ingestion is summarized. Rele
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3.3 DRINKING WATER INGESTION STUDIE
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that the three-day diary has been s
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million. In addition, whites were u
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an indicator of pool water ingestio
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Table 3-4. Per Capita a Estimates o
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Table 3-8. Per Capitaa Estimates of
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Table 3-11. Per Capita a Estimates
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Table 3-14. Consumers Onlya Estimat
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Table 3-18. Consumers Onlya Estimat
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Table 3-21. Consumers Only a Estima
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Water Ingested (mL/day) a from Wate
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Table 3-26. Plain Tap Water and Tot
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Total fluid Plain water Milk Carbon
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Tap Water Intake in Breastfed and F
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Table 3-32. Mean (± Standard Devia
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Study Group Table 3-34. Pool Water
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of specific mouthing events, expres
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Table 4-2. Confidence in Recommenda
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their children’s mouthing behavio
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to mouth activity was recorded duri
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contacts occurring during the objec
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unlikely to be representative of th
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2 to 3 days old, in a quiet, temper
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waking hours. Parents also recorded
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outdoor mouthing rates. The authors
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Activity Data of Two- to Four-Year-
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Table 4-6. Variability in Objects M
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Behavior Child-Specific Exposure Fa
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Table 4-17. Estimated Mean Daily Mo
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Age Group Birth to
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8.3 KEY BODY WEIGHT STUDY 8.3.1 U.S
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III (1966-70) for ages 12-17 years,
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8.4.9 Kahn and Stralka, 2008 - Esti
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Table 8-3. Mean and Percentile Body
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Page Child-Specific Exposure Factor
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Table 8-8. Statistics for Probabili
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Figure 8-2. Weight by Age Percentil
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Figure 8-4. Weight by Length Percen
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Figure 8-6. Body Mass Index-for-Age
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Age Group a Child-Specific Exposure
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Age Group a Child-Specific Exposure
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Source: Gestational Age (weeks) 25
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of the food consumed after the mois
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Minimal (or Defined) Bias Child-Spe
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9.3 INTAKE STUDIES The primary sour
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9.3.2 Relevant Fruit and Vegetable
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Weighted data were used in all of t
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Page Child-Specifi c Exposur e Fact
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Vegetables Any Vegetable Baby Food
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4 to 5 months 6 to 11 months 12 to
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All fruits Canned fruit Fresh fruit
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Table 9-23. Mean Moisture Content o
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eported on fish intake for children
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a Table 10-1. Recommended Values fo
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10.3 GENERAL POPULATION STUDIES 10.
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Minnesota, and North Dakota. While
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elow the value of 8 ounces most com
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into a single pooled data set is so
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as described in Section 10.6.1.2, a
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Columbia River Inter-Tribal Fish Co
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Table 10-12. Fish Consumption Among
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Table 10-18. Mean Fish Intake Among
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Table 10-23. Consumption Rates for
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Species a Anadromous fish Pelagic f
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Lingcod Mackerel, Atlantic Mackerel
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Child-Specific Exposur e Factor s H
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Page 425 and 426: Child-Specific Exposure Factors Han
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National Center for Environmental A
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csefh - Kinder-Umwelt-Gesundheit

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