Overview
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Key numbers
The worker extracted the full PDF text with layout preservation twice and compared extraction hashes before commit. The following lines are copied from numeric/table-bearing regions of the PDF and retain the source units and wording where legible:
- (95% CI, −2.2 to −0.4) on the Boston Naming Test. Standard analyses showed no outcome associations with hair mercury level or fish
- ical exposure assessment. At approximately age 8 years, 607 NBC tests were administered by trained study examiners (n = 2)
- subset (n = 361) with fish-eating mothers, maternal hair mercury Edition (WISC-III),33 the Boston Naming Test (BNT),34 and the
- measurements, and relevant covariate data were the focus of this Wide Range Assessment of Memory and Learning (WRAML).35
- to a mean value of 100 (SD, 15). We analyzed 6 outcomes: WISC-III
- (Table 1). Average mercury content in each of the 8 fish categories intake during pregnancy with offspring cognitive development
- Table 1. Estimated total mercury levels of fish species consumed by the New Bedford Cohort mothers during pregnancy. Total mercury
- b Fraction was based on self-reported (FFQ) species-specific intake during adolescence where available (eg, for adolescents who consumed category 2 fish, 66%
- was bluefish and 34% was mackerel). Where species-specific data were not available, fisheries and/or domestic landings databases were used.
- e On the basis of adolescent data, proportions were 34% mackerel and 66% bluefish. The consumption fraction of mackerel species was obtained from percent
- f On the basis of adolescent data, proportions were 80% canned tuna and 20% fresh tuna. On the basis of National Fisheries Institute data, 75% of canned tuna
- consumed was light and 25% was albacore.23
- high (0.9 ppm), moderate (0.4 ppm), or low (0.1 ppm) levels of hair a particular line under the assumed theoretical relationship.
- Mean (SD) hair mercury level, μg/g 361 0.63 (0.57) 61 0.51 (0.57) .14
- Mean (SD) fish consumption, meals/wk 361 3.78 (3.69) 156 3.52 (4.14) .51
- Mean (SD) umbilical cord serum ΣPCB4 level, ng/g 361 0.26 (0.32) 229 0.25 (0.29) .73
- Breastfed <1 mo, no. (%) 361 213 (59%) 244 168 (68.9%) .02
- Female sex at birth, no. (%) 361 182 (50.4%) 246 117 (47.6%) .54
- Non-Hispanic White race/ethnicity, no. (%) 361 267 (74%) 246 154 (62.6%) <.01
- Mean (SD) age at cognitive testing, y 361 8.11 (0.53) 245 8.25 (0.73) .01
- b For mean values, P values were calculated using a 2-sample t test.
- Table 3. Covariate-adjusteda slopes (and 95% CIs) for the regression of six 8-year neurocognitive outcomes on pregnancy fish intake,
- by tertile of average mercury level in the fish consumed, among New Bedford Cohort participants (n = 361 for all models except
- n = 360 for the Boston Naming Test and General Memory)b
- Table 2 summarizes the distribution of exposures, outcomes, in maternal IQ was associated with a 0.37-point increase (95%
- were included had better test scores and were more likely to be associated, except for the PS subscale (Table 3, Figures 4-6). Con-
- Among the 361 participants with fish-eating mothers (360 with associated with a 0.31-point increase (95% CI, −0.20 to 0.82) in
- BNT and WRAML General Memory scores), the median pregnancy IQ in the lowest AvgFishHg (hair) tertile, a decrease of 0.55 points
- fish intake was 2.3 servings per week, and the mean maternal hair (95% CI, −1.59 to 0.49) in the middle tertile, and a decrease of
- mercury level was 0.63 (range, 0.03-5.14) μg/g. AvgFishHg (hair) 1.22 points (95% CI, −3.11 to 0.67) in the highest tertile. How-
- and AvgFishHg (diet) mercury levels were uncorrelated (Pearson’s ever, all 95% CIs for fish intake associations included the null,
- fish mercury level estimates; 151 (42%) were in the middle tertile among participants consuming fish with the highest average
- (26%) were in the high tertile for one estimate and the low tertile Associations using average fish mercury level estimated from
- Neurocognitive development (Table 3; Figures 4-6). Again, all 95% CIs included the null except
- than that of the test standardization population (mean = 100 with a 0.69-point increase (95% CI, 0.02 to 1.36) for those in the
- (SD, 15)), with mean values of 98 (SD, 13), 90 (SD, 14), and lowest AvgFishHg (diet) tertile.
- C and D) among New Bedford Cohort (NBC) participants assessed at age 8 years whose mothers ate fish during pregnancy (n = 361). NBC participants
- ment for fish or hair mercury level (Table 4; Table S1). of fish intake with an outcome are not independent of fish type.
- and omega-3 PUFA content (derived from surveillance data) neurodevelopmental measures (Table 3). Similarly, the BNT was
- Table 4. Covariate-adjusteda slopes (and 95% CIs) from the regression of six 8-year neurocognitive
- New Bedford Cohort participants (n = 361 for all models except n = 360 for the Boston Naming Test and
-
- Sheslow D, Adams W. WRAML: Wide Range Assessment of Memory years. Neurotoxicol Teratol. 2017;59:35-42. https://doi.org/10.1016/
Methods (brief)
- The study population was a subsample of persons from the
- Biospecimens were collected at birth (umbilical cord blood) and exposure in previous studies, including IQ (particularly verbal
- Maternal hair samples were collected approximately 10 days post-
- incurred during the last trimester of pregnancy.6,17 Samples were
- analyzed by atomic absorption spectroscopy at the Harvard T.H.
- were below the limit of detection (0.05 μg/g hair). Covariate data were collected from questionnaires, medical
- and we used species-specific intake data collected from study also adjusted for the child’s sex, race/ethnicity (non-Hispanic
- were obtained from the published literature,25,26 where sample Statistical analyses and rationale for modeling
- Mean mercury Sample Mean mercury Sample in categoryb
- b For mean values, P values were calculated using a 2-sample t test.
- missing covariate data, for a sample size of 361. associations with outcomes; for example, each point increase
- tion, hair mercury, and infant cognition in a US cohort. Environ school sample: the “Seven Days for My Health” project. Int J
-
- Kipnis V, Midthune D, Freedman L, et al. Bias in dietary-report Elem Res. 2007;119(3):242-254. https://doi.org/10.1007/s12011-
Implications
This page makes the source discoverable for category-level evidence routing. Values remain source-native and should be used only with the stated matrix, species, basis, geography, and censoring context from the paper. The page does not convert total mercury to methylmercury or use total arsenic as inorganic arsenic.
Wiki pages this source may touch
- Canned seafood (with tin flag)
- Fish — marine, predatory (tuna, swordfish, shark, king mackerel)
- Fish — marine, non-predatory (sardines, anchovies, salmon, cod)
- Shellfish (shrimp, crab, lobster, clams, oysters, mussels)
- Mercury
- Mercury
- Cadmium
- Lead
- Arsenic
Verification notes
- Identity check: DOI, raw handle, candidate cite-key, and SHA-256 were compared against existing
wiki/sources/pages before creation. - Full-PDF read:
pdftotext -layoutwas run on the full PDF twice; extracted text hashes matched before the page was written. - Numeric verification: numeric/table-bearing lines were selected mechanically from the verified extraction and preserved without unit conversion or rounding.
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Update history
The five most recent substantive edits to this page, classified major (evidence or structure moved), correction (a published value or statement was wrong and has been fixed), or minor (narrative rewritten without changing the underlying evidence). Each description is derived from what the edit did to this page; the linked commit is the authoritative record, routine regeneration passes are excluded, and the full version history lives in git. When DOI minting comes online (see schema docs), each entry below will also link to a version-pinned DataCite DOI.