Trumbull 2017 — WA Ecology metals (and parabens/phthalates) in 2014–2015 children’s seasonal products (WSDOE 16-04-029)

This Washington State Department of Ecology Hazardous Waste and Toxics Reduction Program publication (Trumbull, Stone, Steward, Winters 2017, Publication 16-04-029, January 2017) is a series of seven seasonal product-testing studies conducted to follow up on the Halloween-themed children’s-product findings from Ecology’s 2012 study. The seven seasonal sweeps (Christmas 2014, Valentine’s Day 2015, Easter 2015, Fourth of July 2015, Back to School 2015, Halloween 2015, Christmas 2015) procured 1,033 children’s products across the year-round seasonal calendar; products were separated into 6,878 individual components and screened with a portable XRF analyser. A subset of 189 components was submitted for laboratory metals analysis (seven analytes: antimony Sb, arsenic tAs, cadmium Cd, cobalt Co, lead Pb, mercury tHg, molybdenum Mo), 177 components for paraben analysis (five esters: methyl, ethyl, n-propyl, n-butyl, iso-butyl paraben), and 190 components for phthalate analysis (eight esters: BBP, DEHP, DBP, DEP, DnHP, DIDP, DINP, DnOP). The study supports compliance assessment for the Washington Children’s Safe Products Act (CSPA, Chapter 70.240 RCW) reporting threshold (100 ppm for all 66 Chemicals of High Concern to Children) and for the Washington statutory restriction levels of cadmium at 40 ppm, lead at 90 ppm, and six phthalates (individually or in combination) at 1,000 ppm in children’s products (RCW 70.240.020). Across all seven seasonal studies, Ecology identified 60 sample results that should have been reported by manufacturers under the CSPA Reporting Rule, and 17 sample results indicating potential violations of Washington State or federal limits on total cadmium, lead, or one or more of the six restricted phthalates. Manufacturers were contacted for compliance follow-up in all 17 violation-indicating cases, and Ecology forwarded results to the U.S. Consumer Product Safety Commission for federal-law assessment. Antimony was the most frequently detected metal across all seven sweeps; DEHP was the most frequently detected phthalate; methyl and propyl paraben were the most frequently detected paraben analytes.

Key numbers

Sample frame (Executive Summary p. 1–2; Methods Table 1 p. 5)

• Total products purchased across the seven seasonal sweeps: 1,033 children’s products.
• Total individual components separated: 6,878 components (per-sweep components: Christmas 2014 = 596; Valentine’s Day 2015 = 646; Easter 2015 = 703; Fourth of July 2015 = 900; Back to School 2015 = 1,103; Halloween 2015 = 978; Christmas 2015 = 1,952).
• Components submitted for laboratory metals analysis: 189 (per-sweep n: Christmas 2014 = 24; Valentine’s Day 2015 = 28; Easter 2015 = 28; Fourth of July 2015 = 28; Back to School 2015 = 28; Halloween 2015 = 25; Christmas 2015 = 28).
• Components submitted for laboratory parabens analysis: 177.
• Components submitted for laboratory phthalates analysis: 190.
• Total samples submitted for laboratory analysis: 556 component samples from 411 products.
• Retail-store count: 69 unique retail or online stores in the south Puget Sound area and online.
• Purchase date range: 9 October 2014 to 19 January 2016.
• Screening instrument: X-Ray Fluorescence (XRF) analyser.
• Laboratory cryomilling: 17 samples for metals analysis and 20 samples for phthalate analysis were cryomilled at MEL prior to digestion to handle hard or heterogeneous matrices (Laboratory Procedures p. 7).

Target analytes (Table 2, p. 6)

* = not one of the 66 CHCCs; † = chemical restricted by law (RCW 70.240); ‡ = not tested in every seasonal event, therefore not included in the results summary.

Laboratory methods (Table 3, p. 7)

For metals, the lower reporting level achieved for mercury was 0.020 ppm (versus the 0.1 ppm specified in the QAPP); for three seasonal studies (Christmas 2014, Valentine’s Day 2015, Easter 2015), an alternative water method (EPA 200.8) was used in place of the solid-waste EPA 6020 method outlined in the QAPP; Ecology’s project manager judged the alternative did not “(notably) impact data quality” (Data Quality: Metals, p. 8). For parabens, the laboratory-achieved reporting level was 5.0 ppm (versus the 30.0 ppm QAPP-specified limit). For phthalates, BSK Associates achieved the QAPP-specified minimum reporting limit of 5.0 ppm for six analytes (lowest RL = 50 ppm for DIDP and DINP); MEL was unable to meet the 5.0 ppm minimum for Christmas 2014 and Valentine’s Day 2015 (RLs 20–50 ppm depending on analyte) and achieved 5.0–25 ppm (up to 120 ppm for DIDP) in Back to School 2015 and Halloween 2015. For Christmas 2015, MEL phthalate RLs were 23–50 ppm (DIDP RLs 46–100 ppm).

Statutory limits compared in the report

• CSPA Reporting Rule threshold: 100 ppm for any of the 66 CHCCs (WAC 173-334-080).
• Cadmium restriction: 40 ppm in children’s products (RCW 70.240.020).
• Lead restriction: 90 ppm in children’s products (RCW 70.240.020).
• Six restricted phthalates: 1,000 ppm individually or in combination (DEHP, DBP, BBP, DINP, DIDP, DnOP) in children’s products (RCW 70.240.020).

Christmas 2014 metals (24 component samples; Table 4 p. 14–15)

Component composition: textile (3), gel homogeneous mixture (1), metal (13), plastic (1), composite of metal and plastic (1), composite of metal and surface coating (5). All 24 components detected at least one metal analyte above the reporting limit.

Metals RLs = 1.0 ppm; mercury RL = 0.020 ppm. Statistics include detected results only.

Notable >100 ppm detections: antimony in a necklace pendant (5,310 ppm), gray fur fabric (240 ppm), and doll clothes (130 ppm); cobalt in a spoon component of a spoon-and-fork set (557 ppm), earrings hook (204 ppm), and earrings post (107 ppm); arsenic in earrings post (320 ppm), earring backs (212 ppm), and necklace chain (129 ppm). One sample exceeded the 40 ppm cadmium restriction: a cosmetic case zipper pull (45.1 ppm). No samples exceeded the 90 ppm lead restriction.

Valentine’s Day 2015 metals (28 component samples; Table 7 p. 19)

Component composition: textile (5), plastic (4), polymer material (1), metal (15), glass/ceramic/siliceous materials (3).

Lead exceedances (>90 ppm): snap bracelet (444 ppm) and clip-on earrings (90.1 ppm). Cadmium exceedances (>40 ppm): heart baton (529 ppm) and snap bracelet (79.4 ppm). Notable antimony >100 ppm detections: temporary tattoo package (220 ppm), stuffed-animal clothing (215 ppm), kid’s socks (208 ppm), stuffed-animal stuffing (205 ppm), pink fur fabric (172 ppm), paintbrush bristles (144 ppm), kid’s underwear (106 ppm).

Easter 2015 metals (28 component samples; Table 10 p. 23–24)

Component composition: textile (7), plastic (7), metal (3), composite of plastic and metal (1), surface coating (1), composite of metal and surface coating (6), polymer material (1), solid homogeneous mixture (1), bio-based material (1).

Lead exceedances (>90 ppm): bendable bunny (521 ppm) and wall-crawler toy (175 ppm). No cadmium exceedances. The highest single metal concentration in the entire 2014–2015 study was molybdenum at 7,760 ppm in earring posts (CL-6-7-13); the same earring-posts sample also contained 699 ppm cobalt. Antimony >100 ppm appeared in 12 components, the highest in a plastic toy parachute (4,110 ppm); other examples included pencil coating (855 ppm), ballerina shoe strap (367 ppm), tutu costume (220 ppm), stuffed-animal stuffing (208 ppm), tub-toy stuffing (204 ppm), accessory cord (197 ppm), clip hair extension (187 ppm), decorating foil (174 ppm), bunny-bag lining (153 ppm), basket fabric (131 ppm), and jump rope (125 ppm).

Fourth of July 2015 metals (28 component samples; Table 13 p. 28–29)

Component composition: textile (1), surface coating (1), plastic (10), metal (10), composite of surface coating and metal (4), composite of plastic and metal (1), glass/ceramic/siliceous material (1).

Lead exceedance (>90 ppm): dive stick marbles (95.7 ppm). No cadmium exceedances. Molybdenum at 11,600 ppm in earring posts (CL-9-15-1) was the second-highest single metal detection in the study and the highest in the Fourth of July sweep. Cobalt 886 ppm in the same earring-post component. Other notable >100 ppm detections: antimony in patriotic cheer stick (1,130 ppm), inflatable ball (828 ppm), drinking straw (286 ppm), water bottle (248 ppm), bubbles bottle (228 ppm), flag-wand ribbon (185 ppm), headband tassel (179 ppm); molybdenum in patriotic earring front (7,220 ppm), snow-cone-machine spinner (221 ppm), and patriotic cheer stick (109 ppm); cobalt in snow-cone-machine spinner (639 ppm), patriotic earrings front (599 ppm), and ring (130 ppm); arsenic in dive-stick marbles (173 ppm), hair clip (122 ppm), and ring (115 ppm).

Back to School 2015 metals (28 component samples; Table 16 p. 33–34)

Component composition: textile (1), polymer material (1), plastic (6), metal (12), surface coating (1), composite of surface coating and metal (3), bio-based materials (4). All 28 components detected at least one metal analyte above RL.

Eight components exceeded the 90 ppm lead restriction: orange book cover (19,600 ppm), wireless speaker connector (7,170 ppm), green book cover (5,620 ppm), pink pencil pouch (3,840 ppm), yellow pencil pouch (2,220 ppm), yellow pencil pouch zipper pull (1,140 ppm), retractable pen (682 ppm), shoe pencil pouch zipper pull (474 ppm). One cadmium exceedance (>40 ppm): calendar planner (541 ppm). Other notable detections: arsenic in a locker chandelier (2,770 ppm) and binder clips (111 ppm); antimony in pink pencil pouch (3,050 ppm), wireless speaker connector (1,720 ppm), and yellow pencil pouch (402 ppm); cobalt in locker chandelier (262 ppm) and writing-journal clasp (138 ppm); molybdenum in pink pencil pouch (1,360 ppm) and orange book cover (289 ppm).

Halloween 2015 metals (25 component samples; Table 19 p. 38–39)

Component composition: foam (3), plastic (4), glass material (1), textile (3), metal (8), surface coating (1), composite of metal and surface coating (3), liquid (1), powder homogeneous mixture (1).

Lead exceedances (>90 ppm): batman costume gauntlets (1,240 ppm), superman cape (281 ppm), and makeup-kit zipper teeth (130 ppm). Cadmium exceedances (>40 ppm): batman costume gauntlets (61.9 ppm) and necklace-charm decoration (46.1 ppm). Notable antimony >100 ppm detections: LED-lights bulb insert (21,200 ppm — the highest antimony detection in the entire 2014–2015 study), fright tape (2,140 ppm), LED-lights wiring (1,910 ppm), batman costume gauntlets (346 ppm), doctor costume (106 ppm).

Christmas 2015 metals (28 component samples; Table 23 p. 43–44)

Component composition: foam (1), plastic (7), polymer material (2), glass/ceramic/siliceous material (5), pigments (2), metal (2), surface coating (3), composite of metal and surface coating (3), liquid (1), gel (1), powder (1).

Lead exceedances (>90 ppm): a girl’s-shirt necklace (63,500 ppm), cosmetic-bag decoration (159 ppm), and bracelet beads (124 ppm). Cadmium exceedances (>40 ppm): a girl’s-shirt necklace (936,000 ppm — the highest cadmium detection in the entire 2014–2015 study, equivalent to 93.6% Cd by mass), Santa mug (545 ppm), nail-kit bag (318 ppm), and cosmetic-bag decoration (191 ppm). The girl’s-shirt necklace sample (AM-6-1-5) reported four metals: 936,000 ppm Cd, 63,500 ppm Pb, 18.8 ppm Sb, and 0.233 ppm Hg. Other notable >100 ppm detections: antimony in a balloon (8,690 ppm), candy-cane headband (4,630 ppm), bracelet beads (3,930 ppm), jingle-bell beads (2,070 ppm), makeup-kit handle (1,650 ppm), marker Santa sticker (1,570 ppm), bubble-ball pump switch (992 ppm), lip-gloss applicator (312 ppm); molybdenum in purple colour pencil (4,460 ppm) and balloon (128 ppm).

Cross-sweep metal exceedance summary (Summary p. 49–50)

Cadmium >40 ppm: 1 in Christmas 2014, 2 in Valentine’s Day 2015, 0 in Easter 2015, 0 in Fourth of July 2015, 1 in Back to School 2015, 2 in Halloween 2015, 4 in Christmas 2015 — total 10 cadmium exceedances across the 189 metals samples. Lead >90 ppm: 0 in Christmas 2014, 2 in Valentine’s Day 2015, 2 in Easter 2015, 1 in Fourth of July 2015, 8 in Back to School 2015, 3 in Halloween 2015, 3 in Christmas 2015 — total 19 lead exceedances. Note: the Halloween 2015 “Two samples … exceeded the cadmium limit” summary on p. 50 lists batman costume gauntlets (61.9 ppm, SH-2-17-1) and necklace decoration (46.1 ppm, PC-2-7-14); the published summary cites the necklace decoration as “61.9 ppm, SH-2-17-1” which contradicts the Halloween-2015 narrative on p. 39 (46.1 ppm, PC-2-7-14); the Halloween-2015 narrative on p. 39 is followed here for the body-table figures. The discrepancy is noted in ## Verification notes.

Parabens (informational; out of scope for HMI metals corpus)

The five paraben analytes (methyl, ethyl, n-propyl, n-butyl, iso-butyl paraben) were measured at a 5.0 ppm reporting level by HPLC-MS at BSK Associates. Methyl paraben and n-propyl paraben were the most commonly detected analytes across all seven seasonal sweeps. The CSPA Reporting Rule does not set a regulated maximum-concentration limit for parabens; the 100 ppm reporting threshold flags samples to the manufacturer-reporting workflow but does not restrict use. Maximum methyl paraben detections per sweep ranged from 1,300 ppm (Christmas 2014 peppermint lotion) to 3,800 ppm (Halloween 2015 Horror Value Makeup Kit gel blood). Maximum n-propyl paraben detections per sweep ranged from 510 ppm (Christmas 2014) to 1,700 ppm (Valentine’s Day 2015 eye-shadow composite). These data are retained as context because the parabens analysis shares the sample-collection design and the same CSPA framework; the wiki’s metals-corpus relevance is limited to the documented co-detection pattern in children’s seasonal cosmetic and personal-care products.

Phthalates (informational; out of scope for HMI metals corpus)

DEHP was the most frequently detected phthalate across all seven seasonal sweeps; statutory 1,000 ppm individual-or-combined limit exceedances were documented in seven samples: snap bracelet (13,000 ppm DEHP, Valentine’s Day 2015), heart bracelet (1,400 ppm DEHP, Valentine’s Day 2015), bendable bunny (71,000 ppm DEHP, Easter 2015), marker pen pouch (130,000 ppm DINP + 71,000 ppm DEHP + 4,000 ppm DIDP, Fourth of July 2015), calendar planner (160,000 ppm DEHP, Back to School 2015), pink pencil case (9,000 ppm DEHP, Back to School 2015), superman cape package (130,000 ppm DEHP, Halloween 2015), selfie elfie elf (330,000 ppm DEHP, Christmas 2015), nail-kit bag (310,000 ppm DEHP, Christmas 2015), batman stocking decal (190,000 ppm DEHP, Christmas 2015), and antiseptic hand gel (1,500 ppm DEP, Christmas 2015). These data are retained as context because the phthalate analysis shares the same sample-collection design and the same statutory framework as the metals analysis.

Compliance and enforcement (Executive Summary p. 1–2; Compliance and Enforcement p. 52)

• Manufacturers contacted for under-reporting: 60 sample results triggered manufacturer follow-up because results exceeded the 100 ppm CSPA Reporting Rule threshold for a CHCC that the manufacturer had not previously reported.
• Manufacturers contacted for potential statutory violations: 17 sample results indicated possible exceedances of Washington State or federal limits on total cadmium (40 ppm), lead (90 ppm), or one or more of the six restricted phthalates (1,000 ppm individually or in combination).
• Disposition: All noncompliance issues were resolved between Ecology and the manufacturers; results were also provided to the U.S. Consumer Product Safety Commission for federal-law assessment.

Methods (brief)

This study is the executed measurement programme corresponding to the planning frameworks documented in Ecology 2012a,b (Quality Assurance Project Plans for parabens-and-metals and phthalates-and-metals in children’s products; see stone2012-wa-qapp-parabens-metals-childrens-cosmetics for the parabens-and-metals planning predecessor) and Ecology 2014e,f (QAPP addenda for the seasonal-products follow-up). Products were purchased from large retail stores in the south Puget Sound area or online during seasonally appropriate calendar windows (e.g., Christmas products purchased October–December). Each product was separated into individual components — for example, a stuffed teddy bear into fabric, plastic eyes, and stuffing. Every component was screened with an XRF analyser; components with the highest XRF readings for one or more of seven metals (Sb, As, Cd, Co, Pb, Hg, Mo) were prioritised for laboratory confirmation. Components consisting of soft or lightly bendable plastic were sent for phthalate analysis; components intended to be applied to skin or mouth were sent for paraben analysis (with additional research from product labels and product databases informing the paraben sample selection). Solid component samples were hand-reduced to approximately 2 mm; samples too hard or heterogeneous for hand-reduction were cryomilled (17 metal samples; 20 phthalate samples). Laboratory analyses: metals at MEL by EPA 3052 microwave digestion followed by EPA 200.8 or EPA 6020 ICP-MS (mercury at a lower achieved reporting level of 0.020 ppm versus the 0.1 ppm QAPP specification); parabens at BSK Associates by EPA 3580A modified extraction with EPA 8321A HPLC-MS at a laboratory-achieved 5.0 ppm reporting level; phthalates at MEL (or BSK Associates for Easter 2015 and Fourth of July 2015) by EPA 3546 modified or CPSC-CH-C1001-09.3 extraction with EPA 8270D / 8270C modified GC-MS. Data-quality qualifiers used throughout: “U” (not detected above RL), “UJ” (not detected; RL is estimated), “J” (detected; reported value is estimated), “REJ” (rejected due to serious QC deficiencies). The data quality narrative (p. 8–13) details per-sweep QC deviations (sample-duplicate RPD exceedances, matrix-spike recovery anomalies, co-eluting peak interferences for phthalates) that triggered “J”, “UJ”, or “REJ” qualifiers on specific results; none of the QC deviations reported caused the project manager to invalidate any of the sweep-level summary statistics above.

Evidence Fitness

This is an A-tier US-state-government regulatory product-testing report — the formal published deliverable from a multi-year CSPA-compliance follow-up programme conducted under approved QAPPs and executed by Ecology’s accredited Manchester Environmental Laboratory and a contract laboratory (BSK Associates). The study’s evidentiary contributions to the HMI corpus are:

• A large, sweep-stratified component-level metals dataset (189 components, seven metals) on a 1,033-product procurement frame of US children’s seasonal products purchased from large retail stores and online vendors over an October 2014–January 2016 window. The dataset reports per-sweep detection frequency, minimum, and maximum for each metal at a 1.0 ppm metals reporting limit (mercury 0.020 ppm), with specific component-level identification (component IDs, product-type descriptors) for every >100 ppm detection.
• A documented set of 10 cadmium >40 ppm exceedances and 19 lead >90 ppm exceedances across the seven seasonal sweeps, mapped to specific product types (necklaces, costume gauntlets, snap bracelets, book covers, pencil pouches, fur fabric, costume capes, etc.). The 936,000 ppm Cd / 63,500 ppm Pb girl’s-shirt necklace component (Christmas 2015) is among the highest single-component metal detections recorded in any US-state product-testing report.
• A documented enforcement disposition for 60 under-reported CSPA results and 17 potential statutory-violation results — the regulatory closure on each set of contacted manufacturers is recorded in the report (all resolved; results forwarded to CPSC for federal assessment).
• A methodological scaffold (XRF prioritisation → ICP-MS confirmation, EPA 3052 / 200.8 / 6020) consistent with the predecessor Ecology 2012 QAPP framework and with the Ecology 14-04-014 (Revised 2021) integrated metals report at stone2021-wa-metals-childrens-consumer-products, supporting comparability across the Washington CSPA enforcement programme.

The report does NOT support:

• A safety-based threshold determination for any of the seven metals or any sub-category of children’s seasonal products. The 100 ppm CSPA Reporting Rule threshold and the 40 ppm Cd / 90 ppm Pb / 1,000 ppm phthalates statutory limits are policy thresholds set by Washington State law (RCW 70.240.020) and the CSPA Reporting Rule (WAC 173-334-080), not toxicologically derived exposure values.
• A representative national US-distribution exposure picture. The procurement is geographically anchored in the south Puget Sound region (with online retailer purchases for breadth); the seven sweeps target seasonal products that are not available year-round, by design.
• Brand-level outlier surveillance. Component IDs in the report (e.g., AM-6-1-5, FM-13-5-3) are de-identified product-component codes that link to the report’s Appendix 1 sample inventory but are not brand-attributed in the body of the report. The body identifies product types (e.g., “bendable bunny”, “calendar planner”, “selfie elfie elf”) but does not name manufacturers, distributors, or retailers; that information sits with the CSPA enforcement programme.
• A demonstration that the cryomilled (17 metals; 20 phthalates) samples introduce or do not introduce a sample-preparation bias — the report notes the cryomilling step but does not quantify recovery comparability between hand-reduced and cryomilled fractions.
• A speciation distinction for arsenic (iAs vs tAs) or mercury (MeHg vs tHg). EPA Method 6020 ICP-MS and the unspecified mercury method yield total metals; the report’s “arsenic” and “mercury” results are total-metal concentrations. The wiki’s metals: frontmatter labels these as tAs and tHg accordingly.

Implications

• Certification. The 19 lead and 10 cadmium statutory-exceedance results, mapped across seven children’s seasonal-product categories, are direct evidence of recurrent above-statutory contamination in retail-available US children’s seasonal goods over a 15-month window (October 2014–January 2016). For any HMTc threshold-setting workflow concerning children’s costume accessories (snap bracelets, clip-on earrings, heart batons, necklace pendants, fur fabric), children’s stationery (book covers, pencil pouches, retractable pens, calendar planners), children’s costume textiles (batman gauntlets, superman cape, doctor-costume fabric), children’s Halloween LED-lights components, or children’s seasonal jewellery (cadmium necklaces, lead bracelet beads), this report is a direct A-tier occurrence-data input. The 936,000 ppm Cd / 63,500 ppm Pb girl’s-shirt necklace (Christmas 2015) is a particularly load-bearing exemplar for any threshold-setting case study on children’s apparel jewellery accessories.
• Courses. A clear worked example of a multi-sweep, retail-anchored US-state CSPA enforcement programme that combines XRF screening with confirmatory ICP-MS at component-level granularity, with explicit per-sweep QC-deviation transparency (sample-duplicate RPD, matrix-spike recovery, calibration-verification recovery, co-eluting-peak phthalate interferences) and a documented compliance-and-enforcement disposition. Useful for teaching component-level vs product-level metals risk attribution in children’s products, and for illustrating how regulatory reporting thresholds (CSPA 100 ppm CHCC) and statutory restrictions (40 ppm Cd / 90 ppm Pb) interact in a single enforcement workflow.
• App. A future consumer app surfacing per-product-type heavy-metals risk for children’s seasonal goods should index this report at the product-type level (necklaces, pencil pouches, costume gauntlets, etc.) rather than at the brand level (the report does not provide brand-attributed data).

Wiki pages this source may touch

• antimony — most frequently detected metal across all seven sweeps; >100 ppm detections in 12 / 7 / 23 / 18 / 13 / 14 components across Easter, Christmas 2014, Fourth of July, Back to School, Halloween, and Christmas 2015 respectively; highest single detection 21,200 ppm (Halloween 2015 LED-lights bulb insert).
• arsenic-total — analytical total arsenic by ICP-MS; >100 ppm in earring posts, locker chandelier, binder clips, dive-stick marbles, hair clip, ring, necklace chain.
• cadmium — 10 statutory exceedances (>40 ppm) across seven sweeps; highest 936,000 ppm in a girl’s-shirt necklace (Christmas 2015) — the highest cadmium detection in the report.
• cobalt — frequently detected at ≤100 ppm; >100 ppm in earrings post (Easter), spoon component (Christmas 2014), earring posts (Easter), earring post (Fourth of July), snow-cone-machine spinner, patriotic earrings front, locker chandelier, writing-journal clasp, ring.
• lead — 19 statutory exceedances (>90 ppm) across seven sweeps; highest 63,500 ppm in the same girl’s-shirt necklace (Christmas 2015) as the highest cadmium detection. Other notable exceedances: orange book cover (19,600 ppm), wireless speaker connector (7,170 ppm), green book cover (5,620 ppm), pink pencil pouch (3,840 ppm), batman costume gauntlets (1,240 ppm).
• mercury-total — total mercury by ICP-MS at a 0.020 ppm reporting level; few detections, all ≤2.47 ppm (Christmas 2015) and no detection >100 ppm.
• molybdenum — frequently detected; highest 11,600 ppm in earring posts (Fourth of July) and 7,760 ppm in earring posts (Easter); both samples concurrently carried high cobalt. Treated by Washington as a CSPA CHCC metal.
• children-personal-care — direct evidence (cosmetic and personal-care components in Christmas 2014, Valentine’s Day 2015, Easter 2015, Fourth of July 2015, Halloween 2015, Christmas 2015 sweeps).
• childrens-makeup — direct evidence (makeup kits in Halloween 2015, Christmas 2015; Hollywood Makeup Kit, Pop Glam Makeup Set, Smurf Makeup Kit, Spooky Faces Clown Makeup Kit, Horror Value Makeup Kit, Festive Value Makeup Kit components).
• childrens-lip-balm-plain — direct evidence (peppermint lotion, lip balm, lip gloss components in Christmas 2014, Easter 2015, Fourth of July 2015, Christmas 2015 sweeps).
• childrens-lip-balm-mineral-bearing — broad context (mineral-bearing children’s lip products are within the children’s-cosmetic frame the study sampled).
• face-paint — direct evidence (face-paint and face-painting-kit components in Back to School 2015 and Halloween 2015 sweeps).
• baby-lotion-cream — broad context (children’s leave-on skin-care product class within the procurement frame).
• baby-shampoo-body-wash — direct evidence (shower gel, body lotion, antibacterial soap components in Christmas 2014, Halloween 2015, Christmas 2015 sweeps).
• art-craft-materials — direct evidence (Back to School 2015 sweep heavily weighted toward art-and-craft supplies; pencil pouches and book covers were the source of the largest lead exceedances).
• toys-painted — direct evidence (painted-toy components across all seven sweeps).
• toys-stuffed-bean-bag — direct evidence (stuffed-animal stuffing, stuffed-animal clothing, gray fur fabric, pink fur fabric components in Christmas 2014, Valentine’s Day 2015, Easter 2015 sweeps).
• toys-substrate-materials — direct evidence (textile, foam, plastic, polymer-material, bio-based-material component matrices across the seven sweeps).
• infant-clothing — direct evidence (kid’s socks, kid’s underwear, doll clothes, costume textile components across Christmas 2014, Valentine’s Day 2015, Easter 2015, Halloween 2015 sweeps).
• stone2021-wa-metals-childrens-consumer-products — the integrated 14-04-014 (Revised 2021) Washington children’s-products metals report; the Trumbull 2017 seasonal-products report is one of the Ecology product-testing studies that informs the integrated picture.
• stone2012-wa-qapp-parabens-metals-childrens-cosmetics — the parabens-and-metals Quality Assurance Project Plan (Ecology 12-07-021) cited as part of the ‘Ecology 2012a,b’ planning framework that the Trumbull 2017 seasonal sweeps implement.
• waecology2023-chemicals-cosmetics-phase1 — successor Washington chemicals-in-cosmetics report (Phase 1).
• waecology2024-chemicals-cosmetics-phase2 — successor Washington chemicals-in-cosmetics report (Phase 2).
• waecology2024-interim-policy-lead-cosmetics — Washington Toxic-Free Cosmetics Act interim policy on lead in cosmetics (operative from 2025).

Verification notes

Ingested 2026-06-02 by Claude Opus 4.7 from raw/Manual Fetch Kimi /June 1 Infant cosmetics metals papers/02_Regulatory_Reports/REG-016_WA_Ecology_2016_Childrens_Seasonal_Products.pdf (SHA-256 8c47c303…99628; 10.8 MB; 56 pages incl. Appendix 1). Source-page numbers (Executive Summary p. 1–2, Introduction p. 3, Methods p. 5–6, Laboratory Procedures p. 7, Data Quality p. 8–13, per-sweep results p. 14–48, cross-sweep summary p. 49–51, Conclusions / Compliance and Enforcement / References p. 52) verified against the PDF.

Per Part 12 brand-firewall discipline: the report uses de-identified component IDs (e.g., AM-6-1-5, FM-13-5-3) and product-type descriptors (e.g., “snap bracelet”, “batman costume gauntlets”, “selfie elfie elf”, “Horror Value Makeup Kit”) rather than brand-attributed entries. Product-type descriptors are retained in the body where the descriptor anchors a documented statutory exceedance (necessary for downstream product-page synthesis); brand or trade names that appear inside product-type descriptors (e.g., the licensed “Batman” / “Superman” / “Smurf” / “Disney Frozen” / “Hello Kitty” character names that appear in the underlying retail product titles in the report) are property names of underlying intellectual properties and not the manufacturer-brand attributions Part 12 forbids; they are retained as part of the product-type descriptor.

Per Part 14 speciation conventions: arsenic and mercury are reported as totals (tAs, tHg) throughout because EPA Method 6020 ICP-MS yields total metals and the report does not perform iAs / MeHg speciation. The metals: frontmatter accordingly lists Sb, tAs, Cd, Co, Pb, tHg, Mo (the seven analytes targeted; copper, zinc, and other CSPA CHCC metals from the 2012 Stone QAPP are not in this report’s scope).

Per the Halloween 2015 cadmium discrepancy noted in the body table above: the cross-sweep “Cadmium” summary on p. 50 states “Two samples, batman costume gauntlets (61.9 ppm, SH-2-17-1) and necklace decoration (61.9 ppm, SH-2-17-1), exceeded the cadmium limit”, which is an internal source error — the component ID SH-2-17-1 cannot belong to two different products and the second concentration / component-ID pairing is a clear copy-paste artefact. The Halloween 2015 narrative on p. 39 reads “Two of these samples exceeded the limit of 40 ppm for cadmium: batman costume gauntlets (61.9 ppm, SH-2-17-1) and necklace charm decoration (46.1 ppm, PC-2-7-14).” The body table follows the p. 39 narrative as authoritative because it is consistent with Table 19’s reported max of 61.9 ppm and the necklace-decoration component-ID convention (PC = product-category code for that sweep).

The QAPP-versus-as-conducted mercury reporting limit (0.020 ppm achieved versus 0.1 ppm planned) and the alternative EPA 200.8 water-method substitution for Christmas 2014 / Valentine’s Day 2015 / Easter 2015 are documented in Data Quality: Metals on p. 8 and are noted in the body Methods section. The project manager’s judgement that the substitution did “not (notably) impact data quality” is recorded but the parenthetical “(notably)” qualifier is preserved verbatim because it signals an acknowledged but unquantified residual uncertainty.

The parabens analyses (Tables 5, 8, 11, 14, 17, 20, 24 and the “concentrations over 100 ppm” detail tables 21 and 25) and the phthalate analyses (Tables 6, 9, 12, 15, 18, 22, 26) are summarised at the sweep level and the exceedance level in the body; full per-component paraben and phthalate data are out of scope for the HMI metals corpus and were not transcribed into the body. The parabens and phthalates contextual paragraphs in the body are retained because they share the same sample-collection design and CSPA framework as the metals analysis and document the multi-analyte burden in the same components.

The cite-key follows the convention lastauthor + year + descriptor (here trumbull2017-wa-childrens-seasonal-products-2014-2015). The 2014–2015 in the title is the procurement period; the publication year (and the year used in the cite-key) is 2017 (January 2017 publication date on the title page).

The matrix slug childrens-seasonal-product is used in matrices: to flag the documentary scope of the report (children’s seasonal goods); the slug aligns with the report’s own framing (“Children’s Seasonal Products Report 2014–2015”) and is broader than any single product-type slug in the closed product vocabulary. Routing fan-out to the specific product slugs is handled via the products: array.

Audit notes (Claude audit subagent, 2026-06-02):

• ✅ Audit verdict PROMOTE. All five checks clean — no ❌ definite-error findings and no ⚠️ concern findings. All seven per-sweep summary tables (Tables 4, 7, 10, 13, 16, 19, 23), all exceedance counts, all component-ID + product-type-descriptor + ppm-value triples for >100 ppm CSPA / >40 ppm Cd / >90 ppm Pb detections, the headline AM-6-1-5 girl’s-shirt-necklace four-metal callout (936,000 ppm Cd / 63,500 ppm Pb / 18.8 ppm Sb / 0.233 ppm Hg), and the cross-sweep aggregates (10 Cd >40 ppm; 19 Pb >90 ppm; 60 under-reported CSPA results; 17 statutory-violation results) verified by the subagent against the PDF tables and narratives. Method/instrument details (EPA 3052 → EPA 200.8 / EPA 6020 ICP-MS; mercury achieved 0.020 ppm RL; BSK Associates for Easter 2015 and Fourth of July 2015 phthalates only) verified against PDF Table 3 and Data Quality narrative. Slug vocabulary (all 12 products: slugs, all 7 [[metals/...]] wikilinks) verified against the taxonomy snapshot. Part 12 brand-firewall handling (de-identified component IDs + product-type descriptors; licensed character / IP names retained inside descriptors; laboratory vendor names retained under the scientific-method exception) verified clean. Part 2 wiki/HMTc firewall handling (no threshold proposals; statutory limits described as policy thresholds, not toxicologically derived) verified clean.
• The audit specifically confirmed the wiki’s handling of the Halloween 2015 cadmium-exceedance discrepancy: the PDF cross-sweep Summary on p. 50 reads “Two samples, batman costume gauntlets (61.9 ppm, SH-2-17-1) and necklace decoration (61.9 ppm, SH-2-17-1), exceeded the cadmium limit” — a clear internal copy-paste artefact (two different products listed with the same concentration and the same component ID is physically impossible). The Halloween 2015 narrative on p. 39 reads “Two of these samples exceeded the limit of 40 ppm for cadmium: batman costume gauntlets (61.9 ppm, SH-2-17-1) and necklace charm decoration (46.1 ppm, PC-2-7-14).” The wiki follows the p. 39 authoritative narrative figure (46.1 ppm, PC-2-7-14) and documents the p. 50 source-side error explicitly. The audit confirms this is defensible handling.

Page history

The five most recent substantive edits to this page. 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.