NOAEL Studies Cosmetic Ingredient

Mercury Compounds NOAEL Studies

INCI: MERCURY COMPOUNDS

CAS: 7439-97-6

Raw No Observed Adverse Effect Level endpoint records grouped by source. This page does not render calculated Margin of Safety values.

Regulatory source 2 endpoints
Source Endpoint Type Value Unit Species Route Duration Study Type Reference
Regulatory source LOAEL (ADJ) =0.009 mg/m^3 - inhalation chronic IRIS chronic inhalation RfC system PoD row_hash=97976ef7cdf518a0; file=iris_rfc_systems.csv; kind=point_of_departure; raw_column=point_of_departure; raw_value=LOAEL (ADJ): 9e-3 mg/m^3; system=Nervous; basis=Hand tremor; increases in memory disturbances; slight subjective and objective evidence of autonomic dysfunction; point_of_departure=LOAEL (ADJ): 9e-3 mg/m^3; composite_uf=30; confidence=Medium; dtxsid=DTXSID1024172; detail_url=https://iris.epa.gov/ChemicalLanding/&substance_nmbr=370; rfc_last_updated=06/01/1995; rfc_pdf_url=https://iris.epa.gov/static/pdfs/0370_summary.pdf
Regulatory source RfC =0.0003 mg/m^3 - inhalation chronic IRIS chronic inhalation RfC system row_hash=3272b8719c732302; file=iris_rfc_systems.csv; kind=reference_value; raw_column=rfc_mg_per_m3; raw_value=3e-4; system=Nervous; basis=Hand tremor; increases in memory disturbances; slight subjective and objective evidence of autonomic dysfunction; point_of_departure=LOAEL (ADJ): 9e-3 mg/m^3; composite_uf=30; confidence=Medium; dtxsid=DTXSID1024172; detail_url=https://iris.epa.gov/ChemicalLanding/&substance_nmbr=370; rfc_last_updated=06/01/1995; rfc_pdf_url=https://iris.epa.gov/static/pdfs/0370_summary.pdf
IARC Monographs 1 endpoint
Source Endpoint Type Value Unit Species Route Duration Study Type Reference
IARC Monographs IARC carcinogenicity classification 3 IARC group - - 1993 IARC Monographs {"additional_info":"volume_publication_year=1993","evaluation_year":1993,"source_table":"iarc_classifications","volume":"58"}
WHO/JECFA 22 endpoints
Source Endpoint Type Value Unit Species Route Duration Study Type Reference
WHO/JECFA LOAEL =0.86 mg/m3 Rat inhalation 11 weeks Reproductive toxicity document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=e0b8d8123d8bbc05; raw_unit=mg/m 3; context=posure to 6 mg/m 3 for up to 11 weeks produced effects that ranged from mild pathological changes to marked cellular degeneration and widespread necrosis (Ashe et al., 1953). (The LOAEL for renal effects was 0.86 mg/m 3 .) Dense deposits in tubule cells and lysosomal inclusions in the renal tubular epithelium were evident following exposure of rats to mercury vapour at 3 mg/m 3 for 3 h/day, 5 days/week, for 12–42 weeks (Kishi et al., 1978).
WHO/JECFA LOAEL =1 mg/m3 Monkey inhalation 5 days Toxicology study document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=cbeb565eb29d092c; raw_unit=mg/m 3; context=avioural tests conducted on the offspring of mother squirrel monkeys that had been exposed during the last two-thirds or more of gestation to mercury vapour concentrations of 0.5 (LOAEL) or 1.0 mg/m 3 for 4 or 7 h/day, 5 days/week, long-term effects included instability in lever-press durations and steady-state performance under concurrent schedules of reinforcement, as well as aberrant transitions (Newland et al., 1996).
WHO/JECFA LOAEL =1.9 mg/kg bw - - 2-year Chronic toxicity document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=5b45b35471d27872; raw_unit=mg/kg body weight; context=Use of a LOAEL of 1.9 mg/kg body weight in a 2-year study as a starting point yields a similar tolerable intake.
WHO/JECFA LOAEL =1.9 mg/kg bw/day - oral long-term Toxicology study document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=b1f23aeba403bc8f; raw_unit=mg/kg body weight per day; context=The LOAEL for renal effects resulting from long-term oral exposure is 1.9 mg/kg body weight per day.
WHO/JECFA LOAEL =8 mg/kg bw/day - - - Toxicology study document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=86144e15aa2ac953; raw_unit=mg/kg body weight per day; context=The NOAEL for males in this study was 1 mg/kg body weight per day; the LOAEL was 8 mg/kg body weight per day for increased liver weights and slight histopathological changes to the renal cortex.
WHO/JECFA LOAEL =9 mg/kg bw - oral - Toxicology study document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=d5556282b3ec8553; raw_unit=mg/kg; context=En partant d’une LOAEL de 1,9 mg/kg de poids corporel obtenue ΰ la suite d’une étude de 2 ans, on parvient à un résultat analogue pour la dose tolérable par ingestion.
WHO/JECFA LOAEL =10 mg/kg bw/day - - - Toxicology study document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=9f23b32e65efe8d7; raw_unit=mg/kg body weight per day; context=The LOAEL for hepatic effects was 10 mg/kg body weight per day.
WHO/JECFA LOAEL =20 mg/kg bw/day - - - Toxicology study document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=10943bffdf1a1cef; raw_unit=mg/kg body weight per day; context=The LOAEL for adrenal effects was 20 mg/kg body weight per day.
WHO/JECFA NOAEL =0.0002 mg/m3 Human inhalation long-term Inhalation toxicity document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=03666409ddfe79c4; raw_unit=ug/m 3; unit_normalization=converted from micrograms; context=Use of uncertainty factors of 10 for interindividual variation in sensitivity to mercury within the human population and 3 for use of a LOAEL (subclinical effects) rather than a NOAEL yields a tolerable concentration of 0.2 ug/m 3 for long-term inhalation exposure to elemental mercury vapour.
WHO/JECFA NOAEL =0.002 mg/m3 - - - Toxicology study document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=e9c963051f76322a; raw_unit=ug/m 3; unit_normalization=converted from micrograms; context=riations interindividuelles et 3 pour l’extrapolation de la dose minimale produisant un effet nocif observable, ou LOAEL (effets légers), à la dose sans effet nocif observable, ou NOAEL), on obtient une concentration tolérable de 0,2 ug/m 3 .
WHO/JECFA NOAEL =0.0328571428571429 mg/kg bw/day Human - 5 days Toxicology study document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=edcb7cf4da5d8fdd; raw_unit=mg/kg body weight per day; unit_normalization=converted from weekly dose; context=Using the NOAEL for renal effects of 0.23 mg/kg body weight per day as the starting point, adjusting the 5 days/week dosing pattern to daily exposure, and applying an uncertainty factor of 100 (10 for extrapolation from animals to humans and 10 for human variability), a tolerable intake of 2 ug/kg body weight per day can be d
WHO/JECFA NOAEL =0.23 mg/kg bw - oral 26-week Toxicology study document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=3673aa1364e39fe3; raw_unit=mg/kg body weight; context=In a 26-week study, a NOAEL for the critical effect, nephrotoxicity, of 0.23 mg/kg body weight was identified for oral exposure to mercuric chloride.
WHO/JECFA NOAEL =0.23 mg/kg bw/day - - - Toxicology study document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=4bed79a183f959d5; raw_unit=mg/kg body weight per day; context=A NOAEL from this study was identified at 0.23 mg/kg body weight per day.
WHO/JECFA NOAEL =1 mg/kg bw/day - - - Toxicology study document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=12e5e1bb9eb84e26; raw_unit=mg/kg body weight per day; context=The NOAEL for males in this study was 1 mg/kg body weight per day; the LOAEL was 8 mg/kg body weight per day for increased liver weights and slight histopathological changes to the renal cortex.
WHO/JECFA NOAEL =23 mg/kg bw - - - Toxicology study document_id=cicads_cicads_cicad50; title=Elemental Mercury and Inorganic Mercury Compounds: Human Health Aspects (Cicads 50, 2003); path=mirror/documents/cicads/cicads/cicad50.htm; row_hash=aa17980b68c2469e; raw_unit=mg/kg; context=Lors d’une étude de 26 semaines avec administration de chlorure mercurique par voie orale, on a obtenu une NOAEL égale à 0,23 mg/kg de poids corporel, l’effet critique considéré étant la néphrotoxicité.
WHO/JECFA NOEL =0.399 mg/g - - - Toxicology study document_id=ehc_ehc_ehc101; title=Methylmercury (EHC 101, 1990); path=mirror/documents/ehc/ehc/ehc101.htm; row_hash=310359be549c8f86; raw_unit=ug/g; unit_normalization=converted from micrograms; context=The lowest level (maximum maternal hair mercury concentration during pregnancy) at which severe effects were observed was 404 ug/g in the Iraqi outbreak and the highest no-observed-effect level for severe effects was 399 ug/g.
WHO/JECFA NOEL =0.399 mg/g - - - Toxicology study document_id=ehc_ehc_ehc101; title=Methylmercury (EHC 101, 1990); path=mirror/documents/ehc/ehc/ehc101.htm; row_hash=310359be549c8f86; raw_unit=ug/g; unit_normalization=converted from micrograms; context=The lowest level (maximum maternal hair mercury concentration during pregnancy) at which severe effects were observed was 404 ug/g in the Iraqi outbreak and the highest no-observed-effect level for severe effects was 399 ug/g.
WHO/JECFA LOAEL =0.05 mg/kg bw Human inhalation - Inhalation toxicity document_id=ehc_ehc_ehc118; title=Mercury, inorganic (EHC 118, 1991); path=mirror/documents/ehc/ehc/ehc118.htm; row_hash=c2964c852ac6c808; raw_unit=mg/kg; context=Using this animal LOAEL (0.05 mg/kg), equivalent human oral and inhalation LOAEL values for kidney effects can be determined as follows:
WHO/JECFA LOAEL =0.05 mg/kg bw Human inhalation - Inhalation toxicity document_id=ehc_ehc_ehc118; title=Mercury, inorganic (EHC 118, 1991); path=mirror/documents/ehc/ehc/ehc118.htm; row_hash=c2964c852ac6c808; raw_unit=mg/kg; context=Using this animal LOAEL (0.05 mg/kg), equivalent human oral and inhalation LOAEL values for kidney effects can be determined as follows:
WHO/JECFA LOAEL =16 mg/kg bw/day - dermal - Toxicology study document_id=ehc_ehc_ehc118; title=Mercury, inorganic (EHC 118, 1991); path=mirror/documents/ehc/ehc/ehc118.htm; row_hash=97f72f2188177f72; raw_unit=mg/kg per day; context=The lowest-observed-adverse-effect level found in these studies was 16 mg/kg per day via the subcutaneous route of exposure.
WHO/JECFA LOAEL =16 mg/kg bw/day - dermal - Toxicology study document_id=ehc_ehc_ehc118; title=Mercury, inorganic (EHC 118, 1991); path=mirror/documents/ehc/ehc/ehc118.htm; row_hash=97f72f2188177f72; raw_unit=mg/kg per day; context=The lowest-observed-adverse-effect level found in these studies was 16 mg/kg per day via the subcutaneous route of exposure.
WHO/JECFA BMDL (10) =0.06 mg/kg bw/day Mouse, Rat oral chronic; 27 weeks chronic LONG_REF=NTP (1993). Toxicology and carcinogenesis studies of mercuric chloride (CAS No. 7487-94-7) in F344 rats and B3C3F1 mice (gavage studies). Research Triangle Park, NC, United States Department of Health and Human Services, National Toxicology Program (NTP Technical Report Series, No. 408).; TITLE=Toxicology and carcinogenesis studies of mercuric chloride (CAS No. 7487-94-7) in F344 rats and B3C3F1 mice (gavage studies); AUTHOR=NTP; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/650affb9e4b0d99f5a8829a0; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://apps.who.int/food-additives-contaminants-jecfa-database/; SUBSOURCE_URL=https://apps.who.int/food-additives-contaminants-jecfa-database/Home/Chemical/1806; YEAR=2011; ORIGINAL_YEAR=2011; TOXICOLOGICAL_EFFECT=Kidney weight changes, proximal tubule damage and progressive nephropathy; STUDY_GROUP=WHO JECFA Tox Studies:15716035:M/F:--; QC_CATEGORY=Manually extracted from unstructured data source; Source overall passed QC, and this record was manually checked; QC_STATUS=pass; SOURCE_HASH=ToxValhc_9b389ba75f7b2a917c65f777d0e295ff
NTP ICE cancer 1 endpoint
Source Endpoint Type Value Unit Species Route Duration Study Type Reference
NTP ICE cancer IARC group 3 unitless - - - WOE; IARC Carcinogenicity sheet=Data; excel_row=1843; Record_ID=cancer_3560; Data_Type=WOE; Formulation_Name=Mercury; Mixture=Chemical; DTXSID=DTXSID1024172; Assay=IARC Carcinogenicity; Endpoint=IARC group; Response=3; Response_Unit=Unitless; URL=http://publications.iarc.fr/76; URL_CompTox=https://comptox.epa.gov/dashboard/chemical/details/DTXSID1024172
ToxValDB ATSDR MRLs 1 endpoint
Source Endpoint Type Value Unit Species Route Duration Study Type Reference
ToxValDB ATSDR MRLs MRL =0.0003 mg/m3 Human inhalation - Toxicity Value STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/674e166be4b0a7c65d36ea5d; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://wwwn.cdc.gov/TSP/MRLS/mrlsListing.aspx; YEAR=2022; ORIGINAL_YEAR=2022; TOXICOLOGICAL_EFFECT=neurological; STUDY_GROUP=ATSDR MRLs:15447149:-:--; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_6c069267df2ef54dc12d1b3663db92e3
ToxValDB Cal OEHHA REL derivations 3 endpoints
Source Endpoint Type Value Unit Species Route Duration Study Type Reference
ToxValDB Cal OEHHA REL derivations LOAEL =0.025 mg/m3 Human inhalation chronic; 15.6 years occupational LONG_REF=Piikivi L and Hanninen H (1989). Subjective symptoms and psychological performance of chlorine-alkali workers. Scand J Work Environ Health 15(1): 69-74. Piikivi L (1989). Cardiovascular reflexes and low long-term exposure to mercury vapour. Int Arch Occup Environ Health 61(6): 391-5. Piikivi L and Tolonen U (1989). EEG findings in chlor-alkali workers subjected to low long term exposure to mercury vapour. Br J Ind Med 46(6): 370-5. Fawer RF, de Ribaupierre Y, Guillemin MP, Berode M and Lob M (1983). Measurement of hand tremor induced by industrial exposure to metallic mercury. Br J Ind Med 40(2): 204-8; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/68c97043e4b02565fc7d32df; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://oehha.ca.gov/; SUBSOURCE_URL=https://oehha.ca.gov/sites/default/files/media/downloads/crnr/appendixd1final.pdf; YEAR=2008; ORIGINAL_YEAR=2008; TOXICOLOGICAL_EFFECT=Neurotoxicity as measured by: intention tremor; memory and sleep disturbances; decreased performance on neurobehavioral tests (finger tapping, visual scan, visuomotor coordination, visual memory); decreased EEG activity; STUDY_GROUP=Cal OEHHA REL derivations:15951890:-:--; QC_CATEGORY=Manually extracted from unstructured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_5f887f2e2470ded2ed685426622bb2ed
ToxValDB Cal OEHHA REL derivations LOAEL =1.8 mg/m3 Rat inhalation (developmental) reproduction developmental LONG_REF=Danielsson BR, Fredriksson A, Dahlgren L, Gardlund AT, Olsson L, Dencker L and Archer T (1993). Behavioural effects of prenatal metallic mercury inhalation exposure in rats. Neurotoxicol Teratol 15(6): 391-6.; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/68c97043e4b02565fc7d32df; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://oehha.ca.gov/; SUBSOURCE_URL=https://oehha.ca.gov/sites/default/files/media/downloads/crnr/appendixd1final.pdf; YEAR=2008; ORIGINAL_YEAR=2008; TOXICOLOGICAL_EFFECT=CNS disturbances in offspring; STUDY_GROUP=Cal OEHHA REL derivations:15951889:-:-pregnant; QC_CATEGORY=Manually extracted from unstructured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_4e87359bf3c46cc2d4f5d7cabec7487e
ToxValDB Cal OEHHA REL derivations NOAEL =0.16 mg Hg/kg-day Rat oral - - LONG_REF=OEHHA. (1999). Public Health Goal for Inorganic Mercury in Drinking Water. Office of Environmental Health Hazard Assessment. California Environmental Protection Agency. Scramento, CA; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/68c97043e4b02565fc7d32df; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://oehha.ca.gov/; SUBSOURCE_URL=https://oehha.ca.gov/sites/default/files/media/downloads/crnr/appendixd1final.pdf; YEAR=2008; ORIGINAL_YEAR=2008; TOXICOLOGICAL_EFFECT=renal toxicity; STUDY_GROUP=Cal OEHHA REL derivations:15951891:-:--; QC_CATEGORY=Manually extracted from unstructured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_9e6e803807c4badda44ca051648500e8
ToxValDB GESTIS DNEL 1 endpoint
Source Endpoint Type Value Unit Species Route Duration Study Type Reference
ToxValDB GESTIS DNEL DNEL systemic =0.02 mg/m3 Human inhalation - Toxicity Value STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/6543dd69e4b045b9ff7cd87e; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://www.dguv.de/ifa/gestis/gestis-dnel-liste/index-2.jsp; STUDY_GROUP=GESTIS DNEL:15633232:-:--; QC_CATEGORY=Programmatically extracted from structured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_521e265aff38422e0e34b00810ecdb36
ToxValDB Health Canada 3 endpoints
Source Endpoint Type Value Unit Species Route Duration Study Type Reference
ToxValDB Health Canada LOAEL =0.317 mg/kg bw/day Rat oral subchronic; 2 months subchronic LONG_REF=Bernaudin et al., 1981; AUTHOR=Bernaudin et al; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/61003a57e4b01a90a3f9c305; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://publications.gc.ca/site/eng/9.694269/publication.html; YEAR=1981; ORIGINAL_YEAR=1981; STUDY_GROUP=Health Canada:15637549:-:--; QC_CATEGORY=Manually extracted from unstructured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_8aed1e85d22cd1fd478cbbccf4333b82
ToxValDB Health Canada LOAEL =0.633 mg/kg bw/day Rat oral subchronic; 2 months subchronic LONG_REF=Andres, 1984; AUTHOR=Andres; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/61003a57e4b01a90a3f9c305; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://publications.gc.ca/site/eng/9.694269/publication.html; YEAR=1984; ORIGINAL_YEAR=1984; STUDY_GROUP=Health Canada:15637550:-:--; QC_CATEGORY=Manually extracted from unstructured data source; Source overall passed QC, but this record was not manually checked; QC_STATUS=not determined; SOURCE_HASH=ToxValhc_a6d6dc15802eb871bc45755124a200ee
ToxValDB Health Canada TDI =0.0003 mg/kg bw/day Human injection subchronic; 8 weeks Toxicity Value LONG_REF=CSQG: CCME, 1999a,b; RfD from U.S. EPA, 1995 (based on several studies, including Druet et al., 1978; Bernaudin et al., 1981; Andres, 1984); STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/61003a57e4b01a90a3f9c305; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://publications.gc.ca/site/eng/9.694269/publication.html; YEAR=1999; ORIGINAL_YEAR=1999; TOXICOLOGICAL_EFFECT=nephrotoxicity; STUDY_GROUP=Health Canada:15637437:-:--; QC_CATEGORY=Manually extracted from unstructured data source; Source overall passed QC, and this record was manually checked; QC_STATUS=pass; SOURCE_HASH=ToxValhc_60d3bc64c6c451b40528f9732021c0eb
ToxValDB IRIS 1 endpoint
Source Endpoint Type Value Unit Species Route Duration Study Type Reference
ToxValDB IRIS LOAEL (ADJ) =0.009 mg/m3 Human inhalation - occupational LONG_REF=Fawer, R.F., U. DeRibaupierre, M.P. Guillemin, M. Berode and M. Lobe. 1983. Measurement of hand tremor induced by industrial exposure to metallic mercury. J. Ind. Med. 40: 204-208. ; Piikivi, L. and U. Tolonen. 1989. EEG findings in chlor-alkali workers subjected to low long term exposure to mercury vapor. Br. J. Ind. Med. 46: 370-375. ; Piikivi, L. and H. Hanninen. 1989. Subjective symptoms and psychological performance of chlorine-alkali workers. Scand. J. Work Environ. Health. 15: 69-74. ; Piikivi, L. 1989. Cardiovascular reflexes and low long-term exposure to mercury vapor. Int. Arch. Occup. Environ. Health. 61: 391-395. ; Ngim, C.H., S.C. Foo, K.W. Boey and J. Jeyaratnam. 1992. Chronic neurobehavioral effects of elemental mercury in dentists. Br. J. Ind. Med. 49: 782-790. ; Liang, Y-X., R-K. Sun, Y. Sun, Z-Q. Chen and L-H. Li. 1993. Psychological effects of low exposure to mercury vapor: Application of a computer-administered neurobehavioral evaluation system. Environ. Res. 60: 320-327.; STORED_SOURCE_RECORD=https://clowder.edap-cluster.com/files/652e8a3be4b045b9ff7a57c8; RECORD_SOURCE_LEVEL=Extraction document; SOURCE_URL=https://www.epa.gov/iris; SUBSOURCE_URL=https://iris.epa.gov/ChemicalLanding/&substance_nmbr=370; TOXICOLOGICAL_EFFECT=Hand tremor|increases in memory disturbances|slight subjective and objective evidence of autonomic dysfunction; STUDY_GROUP=IRIS_dup_IRIS Summary_15645047_15645048:M/F:--; QC_CATEGORY=Manually extracted from unstructured data source; Source overall passed QC, and this record was manually checked; QC_STATUS=pass; SOURCE_HASH=ToxValhc_066df1466f6ea0532195486976c0a5b1
openFDA substances 4 endpoints
Source Endpoint Type Value Unit Species Route Duration Study Type Reference
openFDA substances FDA UNII substance identifier FXS1BY2PGL UNII - - - chemical {"approval_status":null,"molecular_formula":"Hg","source_table":"substance_identifiers_fda","substance_class":"chemical","unii_code":"FXS1BY2PGL"}
openFDA substances FDA UNII substance identifier FXS1BY2PGL UNII - - - chemical {"approval_status":null,"molecular_formula":"Hg","source_table":"substance_identifiers_fda","substance_class":"chemical","unii_code":"FXS1BY2PGL"}
openFDA substances FDA UNII substance identifier FXS1BY2PGL UNII - - - chemical {"approval_status":null,"molecular_formula":"Hg","source_table":"substance_identifiers_fda","substance_class":"chemical","unii_code":"FXS1BY2PGL"}
openFDA substances FDA UNII substance identifier FXS1BY2PGL UNII - - - chemical {"approval_status":null,"molecular_formula":"Hg","source_table":"substance_identifiers_fda","substance_class":"chemical","unii_code":"FXS1BY2PGL"}