{"hq_id":"hq-p-fod-000034","name":"Packaged Breakfast Cereals, Dry Pasta, and Rice in Recycled Paperboard","category":{"primary":"food_contact","secondary":"","tags":[]},"product_tier":"FOD","overall_risk_level":"high","description":"In 2012, food safety authorities in Europe discovered mineral oil migrating from recycled cereal boxes into breakfast cereal. A regulation was proposed to address this.","synthesis":{"derived_risk_level":"moderate","synthesis_confidence":0.658,"synthesis_method":"compound_composition","context_used":"human_child","context_source":"product_users","exposure_modifier":1.173,"vulnerability_escalated":true,"escalation_reason":"Child exposure group","compounds_resolved":4,"compounds_total":4,"synthesis_date":"2026-05-09","synthesis_version":"1.2.0","methodology_note":"exposure_modifier and adjusted_magnitude are computed from ALETHEIA-calibrated heuristics (route × duration × frequency multipliers, clamped to [0.5, 1.4]). Multipliers are directionally informed by EPA Exposure Factors Handbook (2011) and CalEPA OEHHA but are not regulatory consensus. See /api/methodology for full disclosure."},"hazard_summary":{"critical_concern":"EFSA 2012 identified MOSH/MOAH migration from recycled cardboard into breakfast cereals as priority concern (100% detection in samples). No EU or US standard finalized 14 years post-identification. MOSH bioaccumulates in human liver, spleen, kidney. MOAH contains genotoxic PAH (naphthalene, phenanthrene). Barrier film absent in economy-tier brands (50–70% of market). Children eating cereal daily from recycled cardboard receive 3–4× adult cumulative dose normalized to body weight.","key_hazards":["MOSH migration 10–200 µg/kg into cereals from recycled cardboard (100% detection EFSA 2012)","MOAH genotoxicity — aromatic fraction contains IARC 2A/2B PAH","Regulatory stall — 14 years since EFSA concern (2012–2026); no MCL established","Barrier film absent in economy-tier packaging — direct fiber contact allows unrestricted migration","Children highest-exposed population (40 g cereal daily = 400–8,000 µg MOSH/day cumulative dose 3–4× adult normalized)"],"overall_risk":"high","primary_concerns":[],"sensitive_populations":"","exposure_routes":""},"exposure":{"routes":["dermal"],"contact_types":["oral_indirect","ingestion"],"users":["adult","child","pregnant"],"duration":"minutes","frequency":"daily","scenarios":["Incidental mouthing or hand-to-mouth transfer by children","Exposure during pregnancy with potential fetal transfer"],"notes":"Exposure to Packaged Breakfast Cereals, Dry Pasta, and Rice in Recycled Paperboard occurs via dermal. Children and infants face higher exposure per body weight due to developing detoxification systems, higher surface-area-to-weight ratio, and behavioral factors (mouthing, crawling). Pregnant individuals face additional risk from placental transfer of absorbed compounds to the developing fetus."},"consumer_guidance":{"red_flags":[{"indicator":"Contains known carcinogen","meaning":"Mineral oils, untreated and mildly treat — classified by IARC or NTP as carcinogenic or probably carcinogenic to humans","action":"Minimize exposure; consider alternatives; follow use guidelines strictly"},{"indicator":"Overall risk level: high","meaning":"Multiple hazard pathways identified for this product category","action":"Limit exposure duration and frequency; use protective measures where applicable"}],"green_flags":[{"indicator":"Third-party tested for contaminants","meaning":"Independent lab verification of safety claims","verification":"Look for NSF, FDA, or EU compliance certification"}],"what_to_ask":[{"question":"What materials are in direct contact with food?","why_it_matters":"Migration of chemicals from packaging or cookware into food depends on the contact material, temperature, and duration"},{"question":"Has this product been tested for carcinogenic compounds?","why_it_matters":"Products in this category may contain or release carcinogenic compounds; independent testing provides verification beyond manufacturer claims"}],"alternatives":[{"name":"Glass or metal containers","notes":"Non-porous, prevents moisture absorption and contamination risk"},{"name":"Virgin paperboard packaging","notes":"Lower risk of contaminants from recycled materials"}],"notes":null},"regulatory":{"applicable_regulations":[{"jurisdiction":"USA","regulation":"FDA 21 CFR Parts 170–189 (Food Contact Substances)","citation":null,"requirements":"All food-contact materials must comply with FDA regulations for indirect food additives. Materials must not transfer harmful substances to food above established thresholds.","compliance_status":null,"effective_date":null,"enforcing_agency":null,"penalties":null,"source_ref":null},{"jurisdiction":"EU","regulation":"Regulation (EC) No 1935/2004 (Framework Regulation on Food Contact Materials)","citation":null,"requirements":"Materials and articles intended to come into contact with food must not transfer constituents to food in quantities that could endanger human health or bring about unacceptable change in food composition.","compliance_status":null,"effective_date":null,"enforcing_agency":null,"penalties":null,"source_ref":null},{"jurisdiction":"EU","regulation":"Regulation (EU) No 10/2011 (Plastics in Food Contact)","citation":null,"requirements":"Specific migration limits (SMLs) for monomers and additives. Overall migration limit: 10 mg/dm² or 60 mg/kg food. Positive list of authorized substances.","compliance_status":null,"effective_date":null,"enforcing_agency":null,"penalties":null,"source_ref":null},{"jurisdiction":"USA — California","regulation":"California Proposition 65 (Safe Drinking Water and Toxic Enforcement Act)","citation":null,"requirements":"Products containing listed chemicals require clear warning labels if exposure exceeds safe harbor levels. Applies to food packaging, cookware, and food-contact products sold in California.","compliance_status":null,"effective_date":null,"enforcing_agency":null,"penalties":null,"source_ref":null}],"certifications":[{"name":"FDA 21 CFR","issuer":"FDA","standard":"21 CFR Parts 170-199","scope":"Food contact substances, indirect food additives, migration limits"},{"name":"EU 10/2011","issuer":"European Commission","standard":"Regulation (EU) No 10/2011","scope":"Plastic materials intended to come into contact with food"},{"name":"NSF/ANSI 51","issuer":"NSF International","standard":"NSF/ANSI 51 Food Equipment Materials","scope":"Materials used in commercial food equipment"}],"labeling":{"required_disclosures":[],"prop65_warning":{"required":null,"chemicals":[],"endpoint":null,"notes":null},"ghs_labeling":{"required":null,"signal_word":null,"pictograms":[],"hazard_statements":[],"notes":null},"hidden_ingredients":{"trade_secret_protected":null,"categories_hidden":[],"estimated_count":null,"known_concerns":null,"notes":null},"notes":null},"recalls":[],"regulatory_gap":null,"notes":null},"lifecycle":{"recyclable":true,"disposal_guidance":"Recycle by resin code if marked; check local program; food-soiled items may not be accepted","hazardous_waste":false,"expected_lifespan":"1-3_years"},"formulation":{"form":"composite_material","key_ingredients":[{"hq_id":"hq-c-ino-000107","name":"Whole grain flour (wheat, oat, rice — base)","role":"base_material","concentration_pct":"50-80"},{"hq_id":"hq-c-mix-000001","name":"PFAS (from recycled paperboard packaging migration)","role":"additive","concentration_pct":"trace ppb (packaging)"},{"hq_id":"hq-c-ino-000025","name":"Glyphosate residues (pre-harvest desiccant use)","role":"additive","concentration_pct":"trace ppb"},{"hq_id":"hq-c-ino-000047","name":"Iron fortification (added mineral)","role":"active_ingredient","concentration_pct":"0.01-0.05"}],"certifications":[]},"materials":{"common":[{"material_id":"hq-m-str-000086","material_name":"Recycled paperboard food packaging (MOSH/MOAH mineral oil migration)","component":"Food contact packaging; mineral oil contamination from recycled fiber","prevalence":"common"},{"material_id":"hq-m-str-000074","material_name":"","component":null,"prevalence":"common","notes":"Functional barrier film absent in economy-tier packaging (cost reduction); direct fiber-to-food contact increases migration"}],"concerning":[{"material_id":"hq-m-str-000086","concern":"MOSH bioaccumulation in human liver, spleen, kidney — documented in autopsy and occupational exposure studies; MOSH detected at >1 g per organ in individuals with chronic exposure; estimated half-life 100–200 days (slow elimination)","compounds_of_concern":[],"source_refs":[]},{"material_id":"hq-m-str-000086","concern":"MOAH genotoxicity — aromatic fraction contains IARC 2A and 2B PAH (naphthalene, phenanthrene); genotoxic potential not fully characterized; no long-term human carcinogenicity data available","compounds_of_concern":[],"source_refs":[]},{"material_id":"hq-m-str-000086","concern":"Regulatory/labeling gap — consumer cannot distinguish recycled cardboard with barrier film (lower migration) from non-barrier packaging (direct fiber contact). 'Organic cereal' and 'natural product' marketing provides no indication of barrier film presence; organic products equally subject to MOSH contamination as conventional products packaged in recycled cardboard","compounds_of_concern":[],"source_refs":[]},{"material_id":"hq-m-str-000086","concern":"EU regulation stalled 14 years post-EFSA concern (2012–2026) — despite documented MOSH bioaccumulation and MOAH genotoxic potential, no regulatory MCL finalized; MOSH/MOAH migration continues in EU food supply; US FDA has not recognized mineral oil HC as food contaminant","compounds_of_concern":[],"source_refs":[]},{"material_id":"hq-m-str-000086","concern":"Potential contaminant: Mineral oil hydrocarbons (MOSH/MOAH)","compounds_of_concern":[],"source_refs":[]},{"material_id":"hq-m-str-000074","concern":"Cross-contamination from prior use (legacy additives)","compounds_of_concern":["Cross-contamination from prior use (legacy additives)"],"source_refs":[]},{"material_id":"hq-m-str-000074","concern":"Potential contaminant: Cross-contamination from prior use (legacy additives)","compounds_of_concern":[],"source_refs":[]}],"preferred":[]},"compound_composition":[{"hq_id":"hq-c-org-000969","compound_name":"Mineral oil saturated hydrocarbons (MOSH) — C10-C35 alkane fraction","role":"base","typical_concentration":null},{"hq_id":"hq-c-org-000415","compound_name":"Mineral oils, untreated and mildly treated","role":"base","typical_concentration":null},{"hq_id":"hq-c-org-000223","compound_name":"Decabromodiphenyl ether (PBDE-209)","role":"base","typical_concentration":null},{"hq_id":"hq-c-org-000007","compound_name":"Diethylhexyl phthalate (DEHP)","role":"base","typical_concentration":null}],"identifiers":{"common_names":["breakfast cereal box","cereal packaging","pasta box","rice box","recycled cardboard food packaging"],"aliases":[],"manufacturer":null,"brands":[]},"brand_examples":[{"brand":"Generic Mass-Market Brand A","manufacturer":"Consumer Products Corporation","market_position":"mass_market","notable":"Widely available mass-market option"},{"brand":"Generic Mass-Market Brand B","manufacturer":"Consumer Goods Ltd","market_position":"mass_market","notable":"Popular budget alternative"},{"brand":"Premium Brand A","manufacturer":"Premium Consumer Inc","market_position":"premium","notable":"Upscale premium positioning"},{"brand":"Professional Brand","manufacturer":"Professional Products Co","market_position":"professional","notable":"Professional/salon-grade option"},{"brand":"Specialty Eco-Brand","manufacturer":"Natural Products Ltd","market_position":"premium","notable":"Sustainable/natural product line"}],"brand_examples_disclaimer":"Representative branded products of this category. Concerning ingredients listed in materials.concerning[] apply to the category, not necessarily to every named brand. Specific formulations vary by SKU and may have changed since this record was written; consult the brand's current ingredient label before drawing brand-level conclusions.","sources":[{"id":"src_001","type":"regulatory","title":"EFSA (2012) — Mineral Oil HC in Food; 14-Year Regulatory Stall","year":2012,"notes":"100% detection; MOSH bioaccumulation documented; no final regulation enacted"},{"type":"regulation","title":"FDA 21 CFR Parts 170–189 (Food Contact Substances)","jurisdiction":"USA","id":"src_236ea76c"},{"type":"regulation","title":"Regulation (EC) No 1935/2004 (Framework Regulation on Food Contact Materials)","jurisdiction":"EU","id":"src_5c7d1067"},{"type":"regulation","title":"Regulation (EU) No 10/2011 (Plastics in Food Contact)","jurisdiction":"EU","id":"src_acd69b29"},{"type":"regulation","title":"California Proposition 65 (Safe Drinking Water and Toxic Enforcement Act)","jurisdiction":"USA — California","id":"src_a6f0bc64"},{"id":"niosh_metalworking_fluids_1998","type":"regulatory","title":"NIOSH Criteria Document: Occupational Exposure to Metalworking Fluids — Mineral Oil Cutting Fluids; PAH Skin Carcinogenicity; Biological Monitoring; Recommendations for Severely Hydrotreated Oils","year":1998,"inherited_from_compound":"hq-c-org-000415"},{"id":"iarc_mineraloils_vol100f_2012","type":"iarc_monograph","title":"IARC Monographs Volume 100F: Mineral Oils (Untreated and Mildly Treated) — Group 1; British Mule Spinner Scrotal Cancer; PAH Content; Hydrotreatment Degree and Carcinogenicity; Highly Refined Oils Group 3","year":2012,"inherited_from_compound":"hq-c-org-000415"},{"id":"stockholm_decabde_2017","type":"regulatory","title":"Stockholm Convention: Decabromodiphenyl Ether (DecaBDE) Listed under Annex A (Elimination), COP-8 Decision SC-8/12, Debromination Concern, Arctic Contamination, RoHS Interaction, Aircraft Exemptions (2017)","year":2017,"inherited_from_compound":"hq-c-org-000223"},{"id":"eu_rohs_decabde","type":"regulatory","title":"EU Directive 2011/65/EU (RoHS Recast): DecaBDE Restricted in EEE; DecaBDE REACH SVHC Identification; Debromination Products BDE-47/BDE-99 Metabolite Pathway in Humans and Wildlife (2011)","year":2011,"inherited_from_compound":"hq-c-org-000223"},{"type":"report","citation":"Environmental Working Group. Polluted Pets: High Levels of Toxic Industrial Chemicals Contaminate Cats and Dogs. 2008.","url":"https://www.ewg.org/research/polluted-pets","id":"ewg_2008","inherited_from_compound":"hq-c-org-000007"},{"type":"report","citation":"Danish Ministry of the Environment. Survey of phthalates in dog toys. 2006.","id":"danish_study","inherited_from_compound":"hq-c-org-000007"}],"meta":{"schema_version":"4.0.0","last_updated":"2026-03-25","timestamp":"2026-05-13T22:24:00.428Z"}}