MOBILE VIEW  | 

GERMANIUM HYDRIDES

Classification   |    Detailed evidence-based information

Therapeutic Toxic Class

    A) Germanium tetrahydride is a colorless gas which is related structurally and toxicologically to stibine and arsine (ACGIH, 1992).
    B) Other germanium hydrides correspond to the methane series of hydrocarbons and to silanes (Clayton & Clayton, 1994).

Specific Substances

    A) GERMANIUM TETRAHYDRIDE
    1) Germane
    2) Monogermane
    3) Germanium hydride
    4) Germanomethane
    5) NIOSH/RTECS LY 4900000
    6) CAS 7782-65-2
    7) Molecular Formula: Ge-H4
    GERMANOETHANE
    1) Digermane
    2) Molecular Formula: Ge2-H6
    GERMANOPROPANE
    1) Trigermane
    2) Molecular Formula: Ge3-H8

Available Forms Sources

    A) USES
    1) Germanium tetrahydride is used as a doping agent for solid state electronics (ACGIH, 1992).

Life Support

    A) This overview assumes that basic life support measures have been instituted.

Clinical Effects

    0.2.1) SUMMARY OF EXPOSURE
    A) Germanium tetrahydride is a hemolytic agent similar to arsine and stibine. Germanium hydrides are GASES.
    0.2.7) NEUROLOGIC
    A) Seizures, excitation, and locomotor impairment were seen in experimental animals fatally poisoned with 2 g/m(3).
    0.2.10) GENITOURINARY
    A) Degenerative epithelium changes were seen in experimental animals exposed to high-level inhalation. Hemoglobinuria was observed in guinea pigs given high concentrations.
    0.2.13) HEMATOLOGIC
    A) Hemolysis was noted in exposed experimental animals. Germanium hydride has hemolytic potency less than that of arsine. No human cases have been reported.
    0.2.20) REPRODUCTIVE
    A) No teratogenic effects were seen with various germanium salts.

Laboratory Monitoring

    A) These agents may cause renal toxicity. Monitor renal function tests and urinalysis.
    B) If hemolysis is suspected, monitor hemoglobin, hematocrit, serum free hemoglobin, and haptoglobin.

Treatment Overview

    0.4.3) INHALATION EXPOSURE
    A) Human exposure cases have not been reported. Experimental animal data would indicate symptomatic support for seizures and renal function monitoring. Since little is known of human exposures, patients should be closely observed.
    B) INHALATION: Move patient to fresh air. Monitor for respiratory distress. If cough or difficulty breathing develops, evaluate for respiratory tract irritation, bronchitis, or pneumonitis. Administer oxygen and assist ventilation as required. Treat bronchospasm with an inhaled beta2-adrenergic agonist. Consider systemic corticosteroids in patients with significant bronchospasm.
    C) SEIZURES: Administer a benzodiazepine; DIAZEPAM (ADULT: 5 to 10 mg IV initially; repeat every 5 to 20 minutes as needed. CHILD: 0.1 to 0.5 mg/kg IV over 2 to 5 minutes; up to a maximum of 10 mg/dose. May repeat dose every 5 to 10 minutes as needed) or LORAZEPAM (ADULT: 2 to 4 mg IV initially; repeat every 5 to 10 minutes as needed, if seizures persist. CHILD: 0.05 to 0.1 mg/kg IV over 2 to 5 minutes, up to a maximum of 4 mg/dose; may repeat in 5 to 15 minutes as needed, if seizures continue).
    1) Consider phenobarbital or propofol if seizures recur after diazepam 30 mg (adults) or 10 mg (children greater than 5 years).
    2) Monitor for hypotension, dysrhythmias, respiratory depression, and need for endotracheal intubation. Evaluate for hypoglycemia, electrolyte disturbances, and hypoxia.
    D) HEMOLYSIS - Hemolysis has not been reported in exposed humans. If suspected, monitor hemoglobin and hematocrit. Transfusion of blood or packed RBCs might be needed. Maintain a brisk urine output to avoid kidney damage from deposition of RBC breakdown products.
    0.4.4) EYE EXPOSURE
    A) DECONTAMINATION: Remove contact lenses and irrigate exposed eyes with copious amounts of room temperature 0.9% saline or water for at least 15 minutes. If irritation, pain, swelling, lacrimation, or photophobia persist after 15 minutes of irrigation, the patient should be seen in a healthcare facility.

Range Of Toxicity

    A) Mice were killed at concentrations of 150 and 185 ppm for 1 hour by inhalation of germanium tetrahydride.
    B) Inhalation of 100 ppm for 1 hour was survived by a rabbit.
    C) The higher germanes (germanoethane and germanopropane) are thought to be less toxic than germane.

Summary Of Exposure

    A) Germanium tetrahydride is a hemolytic agent similar to arsine and stibine. Germanium hydrides are GASES.

Vital Signs

    3.3.3) TEMPERATURE
    A) HYPOTHERMIA was seen in fatally poisoned rats given 2 g/m(3) (Gus'Kova, 1960).

Respiratory

    3.6.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    a) No local respiratory effects were seen after inhalation of germanium tetrahydride in acute or chronic studies in experimental animals (Stokinger, 1981).

Neurologic

    3.7.1) SUMMARY
    A) Seizures, excitation, and locomotor impairment were seen in experimental animals fatally poisoned with 2 g/m(3).
    3.7.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    a) Excitation, locomotor impairment, and seizures were seen in fatally poisoned rats exposed to 2 gm/m(3) (Gus'Kova, 1960).

Genitourinary

    3.10.1) SUMMARY
    A) Degenerative epithelium changes were seen in experimental animals exposed to high-level inhalation. Hemoglobinuria was observed in guinea pigs given high concentrations.
    3.10.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    a) TUBULE DAMAGE - Degenerative epithelium changes were seen in experimental animals exposed by inhalation to high levels of germanium hydrides (Vouk, 1979).
    2) RENAL FUNCTION ABNORMAL
    a) HEMOGLOBINURIA was observed in guinea pigs given high concentrations of germane (Paneth & Joachimoglu, 1924).

Hematologic

    3.13.1) SUMMARY
    A) Hemolysis was noted in exposed experimental animals. Germanium hydride has hemolytic potency less than that of arsine. No human cases have been reported.
    3.13.3) ANIMAL EFFECTS
    A) ANIMAL STUDIES
    a) Paneth & Joachimoglu (1924) performed animal experiments that demonstrated that germanium hydride was a hemolytic gas with potency less than that of arsine, but capable of producing death in rodents. No human cases have been reported.

Reproductive

    3.20.1) SUMMARY
    A) No teratogenic effects were seen with various germanium salts.
    3.20.2) TERATOGENICITY
    A) LACK OF EFFECT
    1) No teratogenic effects were seen with various germanium salts. Germanium tetrahydride was not specifically tested (Schardein, 1993).

Carcinogenicity

    3.21.1) IARC CATEGORY
    A) IARC Carcinogenicity Ratings for CAS7782-65-2 (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004):
    1) Not Listed

Monitoring Parameters Levels

    4.1.1) SUMMARY
    A) These agents may cause renal toxicity. Monitor renal function tests and urinalysis.
    B) If hemolysis is suspected, monitor hemoglobin, hematocrit, serum free hemoglobin, and haptoglobin.
    4.1.2) SERUM/BLOOD
    A) BLOOD/SERUM CHEMISTRY
    1) "Normal" germanium blood levels are estimated at 0.2 to 0.29 mcg/mL (Hamilton et al, 1972/73; (Schroeder & Balassa, 1967).
    2) These agents may cause renal toxicity. Monitor renal function tests and urinalysis in patients with significant exposure.
    4.1.3) URINE
    A) URINALYSIS
    1) These agents may cause renal toxicity. Monitor renal function tests and urinalysis in patients with significant exposure.

Methods

    A) MULTIPLE ANALYTICAL METHODS
    1) The methods most commonly used to analyze germanium in environmental and biologic samples include, atomic absorption spectroscopy, emission spectrography, and spectrophotometry with phenylfluorone (Vouk, 1979). The limit of detection of AAS is 1.5 mg/L, and may be decreased to 0.015 mg/L by using a graphite tube atomizer (Vouk, 1979).
    2) Germanium and tin can be simultaneously determined on a bifunctional ion-exchange column with chromogenic reaction and spectrophotometric detection at 520 nm. Lower limits of sensitivity are in the low mcg/L range (Sun et al, 1995).

Life Support

    A) Support respiratory and cardiovascular function.

Monitoring

    A) These agents may cause renal toxicity. Monitor renal function tests and urinalysis.
    B) If hemolysis is suspected, monitor hemoglobin, hematocrit, serum free hemoglobin, and haptoglobin.

Inhalation Exposure

    6.7.1) DECONTAMINATION
    A) Move patient from the toxic environment to fresh air. Monitor for respiratory distress. If cough or difficulty in breathing develops, evaluate for hypoxia, respiratory tract irritation, bronchitis, or pneumonitis.
    B) OBSERVATION: Carefully observe patients with inhalation exposure for the development of any systemic signs or symptoms and administer symptomatic treatment as necessary.
    C) INITIAL TREATMENT: Administer 100% humidified supplemental oxygen, perform endotracheal intubation and provide assisted ventilation as required. Administer inhaled beta-2 adrenergic agonists, if bronchospasm develops. Consider systemic corticosteroids in patients with significant bronchospasm (National Heart,Lung,and Blood Institute, 2007). Exposed skin and eyes should be flushed with copious amounts of water.
    6.7.2) TREATMENT
    A) SEIZURE
    1) SUMMARY
    a) Attempt initial control with a benzodiazepine (eg, diazepam, lorazepam). If seizures persist or recur, administer phenobarbital or propofol.
    b) Monitor for respiratory depression, hypotension, and dysrhythmias. Endotracheal intubation should be performed in patients with persistent seizures.
    c) Evaluate for hypoxia, electrolyte disturbances, and hypoglycemia (or, if immediate bedside glucose testing is not available, treat with intravenous dextrose).
    2) DIAZEPAM
    a) ADULT DOSE: Initially 5 to 10 mg IV, OR 0.15 mg/kg IV up to 10 mg per dose up to a rate of 5 mg/minute; may be repeated every 5 to 20 minutes as needed (Brophy et al, 2012; Prod Info diazepam IM, IV injection, 2008; Manno, 2003).
    b) PEDIATRIC DOSE: 0.1 to 0.5 mg/kg IV over 2 to 5 minutes; up to a maximum of 10 mg/dose. May repeat dose every 5 to 10 minutes as needed (Loddenkemper & Goodkin, 2011; Hegenbarth & American Academy of Pediatrics Committee on Drugs, 2008).
    c) Monitor for hypotension, respiratory depression, and the need for endotracheal intubation. Consider a second agent if seizures persist or recur after repeated doses of diazepam .
    3) NO INTRAVENOUS ACCESS
    a) DIAZEPAM may be given rectally or intramuscularly (Manno, 2003). RECTAL DOSE: CHILD: Greater than 12 years: 0.2 mg/kg; 6 to 11 years: 0.3 mg/kg; 2 to 5 years: 0.5 mg/kg (Brophy et al, 2012).
    b) MIDAZOLAM has been used intramuscularly and intranasally, particularly in children when intravenous access has not been established. ADULT DOSE: 0.2 mg/kg IM, up to a maximum dose of 10 mg (Brophy et al, 2012). PEDIATRIC DOSE: INTRAMUSCULAR: 0.2 mg/kg IM, up to a maximum dose of 7 mg (Chamberlain et al, 1997) OR 10 mg IM (weight greater than 40 kg); 5 mg IM (weight 13 to 40 kg); INTRANASAL: 0.2 to 0.5 mg/kg up to a maximum of 10 mg/dose (Loddenkemper & Goodkin, 2011; Brophy et al, 2012). BUCCAL midazolam, 10 mg, has been used in adolescents and older children (5-years-old or more) to control seizures when intravenous access was not established (Scott et al, 1999).
    4) LORAZEPAM
    a) MAXIMUM RATE: The rate of intravenous administration of lorazepam should not exceed 2 mg/min (Brophy et al, 2012; Prod Info lorazepam IM, IV injection, 2008).
    b) ADULT DOSE: 2 to 4 mg IV initially; repeat every 5 to 10 minutes as needed, if seizures persist (Manno, 2003; Brophy et al, 2012).
    c) PEDIATRIC DOSE: 0.05 to 0.1 mg/kg IV over 2 to 5 minutes, up to a maximum of 4 mg/dose; may repeat in 5 to 15 minutes as needed, if seizures continue (Brophy et al, 2012; Loddenkemper & Goodkin, 2011; Hegenbarth & American Academy of Pediatrics Committee on Drugs, 2008; Sreenath et al, 2009; Chin et al, 2008).
    5) PHENOBARBITAL
    a) ADULT LOADING DOSE: 20 mg/kg IV at an infusion rate of 50 to 100 mg/minute IV. An additional 5 to 10 mg/kg dose may be given 10 minutes after loading infusion if seizures persist or recur (Brophy et al, 2012).
    b) Patients receiving high doses will require endotracheal intubation and may require vasopressor support (Brophy et al, 2012).
    c) PEDIATRIC LOADING DOSE: 20 mg/kg may be given as single or divided application (2 mg/kg/minute in children weighing less than 40 kg up to 100 mg/min in children weighing greater than 40 kg). A plasma concentration of about 20 mg/L will be achieved by this dose (Loddenkemper & Goodkin, 2011).
    d) REPEAT PEDIATRIC DOSE: Repeat doses of 5 to 20 mg/kg may be given every 15 to 20 minutes if seizures persist, with cardiorespiratory monitoring (Loddenkemper & Goodkin, 2011).
    e) MONITOR: For hypotension, respiratory depression, and the need for endotracheal intubation (Loddenkemper & Goodkin, 2011; Manno, 2003).
    f) SERUM CONCENTRATION MONITORING: Monitor serum concentrations over the next 12 to 24 hours. Therapeutic serum concentrations of phenobarbital range from 10 to 40 mcg/mL, although the optimal plasma concentration for some individuals may vary outside this range (Hvidberg & Dam, 1976; Choonara & Rane, 1990; AMA Department of Drugs, 1992).
    6) OTHER AGENTS
    a) If seizures persist after phenobarbital, propofol or pentobarbital infusion, or neuromuscular paralysis with general anesthesia (isoflurane) and continuous EEG monitoring should be considered (Manno, 2003). Other anticonvulsants can be considered (eg, valproate sodium, levetiracetam, lacosamide, topiramate) if seizures persist or recur; however, there is very little data regarding their use in toxin induced seizures, controlled trials are not available to define the optimal dosage ranges for these agents in status epilepticus (Brophy et al, 2012):
    1) VALPROATE SODIUM: ADULT DOSE: An initial dose of 20 to 40 mg/kg IV, at a rate of 3 to 6 mg/kg/minute; may give an additional dose of 20 mg/kg 10 minutes after loading infusion. PEDIATRIC DOSE: 1.5 to 3 mg/kg/minute (Brophy et al, 2012).
    2) LEVETIRACETAM: ADULT DOSE: 1000 to 3000 mg IV, at a rate of 2 to 5 mg/kg/min IV. PEDIATRIC DOSE: 20 to 60 mg/kg IV (Brophy et al, 2012; Loddenkemper & Goodkin, 2011).
    3) LACOSAMIDE: ADULT DOSE: 200 to 400 mg IV; 200 mg IV over 15 minutes (Brophy et al, 2012). PEDIATRIC DOSE: In one study, median starting doses of 1.3 mg/kg/day and maintenance doses of 4.7 mg/kg/day were used in children 8 years and older (Loddenkemper & Goodkin, 2011).
    4) TOPIRAMATE: ADULT DOSE: 200 to 400 mg nasogastric/orally OR 300 to 1600 mg/day orally divided in 2 to 4 times daily (Brophy et al, 2012).
    B) HEMOLYSIS
    1) Hemolysis has NOT been reported in exposed humans.
    2) If suspected, monitor hemoglobin, hematocrit, serum free hemoglobin, and haptoglobin.
    3) Transfusion of blood or packed RBCs might be required in serious cases.
    4) Maintenance of a brisk urine output and urine alkalinization with a sodium bicarbonate infusion could be required to prevent kidney damage from deposition of RBC breakdown products.

Eye Exposure

    6.8.1) DECONTAMINATION
    A) EYE IRRIGATION, ROUTINE: Remove contact lenses and irrigate exposed eyes with copious amounts of room temperature 0.9% saline or water for at least 15 minutes. If irritation, pain, swelling, lacrimation, or photophobia persist after 15 minutes of irrigation, an ophthalmologic examination should be performed (Peate, 2007; Naradzay & Barish, 2006).
    6.8.2) TREATMENT
    A) GENERAL TREATMENT
    1) Treatment should include recommendations listed in the INHALATION EXPOSURE section when appropriate.

Dermal Exposure

    6.9.1) DECONTAMINATION
    A) DERMAL DECONTAMINATION
    1) DECONTAMINATION: Remove contaminated clothing and wash exposed area thoroughly with soap and water for 10 to 15 minutes. A physician may need to examine the area if irritation or pain persists (Burgess et al, 1999).
    6.9.2) TREATMENT
    A) GENERAL TREATMENT
    1) Treatment should include recommendations listed in the INHALATION EXPOSURE section when appropriate.

Summary

    A) Mice were killed at concentrations of 150 and 185 ppm for 1 hour by inhalation of germanium tetrahydride.
    B) Inhalation of 100 ppm for 1 hour was survived by a rabbit.
    C) The higher germanes (germanoethane and germanopropane) are thought to be less toxic than germane.

Minimum Lethal Exposure

    A) SPECIFIC SUBSTANCE
    1) GERMANIUM TETRAHYDRIDE -
    a) EXPERIMENTAL ANIMALS - Mice were killed at concentrations of 150 and 185 parts per million for 1 hour by inhalation; a guinea pig died after exposure to 185 parts per million for 1 hour (ACGIH, 1992).
    b) EXPERIMENTAL ANIMALS - 610 micrograms/cubic meter for 30 minutes was lethal in mice; 480 micrograms/cubic meter for 60 minutes was lethal in mice, but not in hamsters (Stokinger, 1981).

Maximum Tolerated Exposure

    A) SPECIFIC SUBSTANCE
    1) GERMANIUM TETRAHYDRIDE -
    a) ANIMALS - 100 parts per million for 1 hour by inhalation was survived by a rabbit. A similar 1 hour inhalation exposure to 150 parts per million sickened a guinea pig (ACGIH, 1992). A concentration of 310 micrograms/cubic meter for 60 minutes by inhalation produced dyspnea, but not death, in a rabbit (Stokinger, 1981).
    b) The higher germanes (germanoethane & germanopropane) are thought to be less toxic than germane (Stokinger, 1981).
    c) Non-specific and non-persistent changes were seen in the kidneys, blood, and CNS when experimental animals were exposed to 70 micrograms/cubic meter for 2 to 15 days (Stokinger, 1981).

Workplace Standards

    A) ACGIH TLV Values for CAS7782-65-2 (American Conference of Governmental Industrial Hygienists, 2010):
    1) Editor's Note: The listed values are recommendations or guidelines developed by ACGIH(R) to assist in the control of health hazards. They should only be used, interpreted and applied by individuals trained in industrial hygiene. Before applying these values, it is imperative to read the introduction to each section in the current TLVs(R) and BEI(R) Book and become familiar with the constraints and limitations to their use. Always consult the Documentation of the TLVs(R) and BEIs(R) before applying these recommendations and guidelines.
    a) Adopted Value
    1) Germanium tetrahydride
    a) TLV:
    1) TLV-TWA: 0.2 ppm
    2) TLV-STEL:
    3) TLV-Ceiling:
    b) Notations and Endnotes:
    1) Carcinogenicity Category: Not Listed
    2) Codes: Not Listed
    3) Definitions: Not Listed
    c) TLV Basis - Critical Effect(s): Hematologic eff
    d) Molecular Weight: 76.63
    1) For gases and vapors, to convert the TLV from ppm to mg/m(3):
    a) [(TLV in ppm)(gram molecular weight of substance)]/24.45
    2) For gases and vapors, to convert the TLV from mg/m(3) to ppm:
    a) [(TLV in mg/m(3))(24.45)]/gram molecular weight of substance
    e) Additional information:

    B) NIOSH REL and IDLH Values for CAS7782-65-2 (National Institute for Occupational Safety and Health, 2007):
    1) Listed as: Germanium tetrahydride
    2) REL:
    a) TWA: 0.2 ppm (0.6 mg/m(3))
    b) STEL:
    c) Ceiling:
    d) Carcinogen Listing: (Not Listed) Not Listed
    e) Skin Designation: Not Listed
    f) Note(s):
    3) IDLH: Not Listed

    C) Carcinogenicity Ratings for CAS7782-65-2 :
    1) ACGIH (American Conference of Governmental Industrial Hygienists, 2010): Not Listed ; Listed as: Germanium tetrahydride
    2) EPA (U.S. Environmental Protection Agency, 2011): Not Listed
    3) IARC (International Agency for Research on Cancer (IARC), 2016; International Agency for Research on Cancer, 2015; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2010a; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2008; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2007; IARC Working Group on the Evaluation of Carcinogenic Risks to Humans, 2006; IARC, 2004): Not Listed
    4) NIOSH (National Institute for Occupational Safety and Health, 2007): Not Listed ; Listed as: Germanium tetrahydride
    5) MAK (DFG, 2002): Not Listed
    6) NTP (U.S. Department of Health and Human Services, Public Health Service, National Toxicology Project ): Not Listed

    D) OSHA PEL Values for CAS7782-65-2 (U.S. Occupational Safety, and Health Administration (OSHA), 2010):
    1) Not Listed

Toxicologic Mechanism

    A) Germanium itself causes a profound water imbalance at high exposure levels that leads to dehydration, hemoconcentration, hypotension, and hypothermia (Stokinger, 1981).
    B) Germanium tetrahydride is a hemolytic agent of intermediate toxicity between that of stibine and arsine (Clayton & Clayton, 1994; ACGIH, 1992).

Physical Characteristics

    A) GERMANIUM TETRAHYDRIDE: Is a colorless gas with a nauseating odor (Webster, 1946; (ACGIH, 1992).

Molecular Weight

    A) GERMANIUM TETRAHYDRIDE: 76.63
    B) GERMANOETHANE: 151.23
    C) GERMANOPROPANE: 225.83

General Bibliography

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    2) 40 CFR 372.65: Environmental Protection Agency - Toxic Chemical Release Reporting, Community Right-To-Know, Chemicals and Chemical Categories to which this part applies. National Archives and Records Association (NARA) and the Government Printing Office (GPO), Washington, DC. Final rules current as of Apr 3, 2006.
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