Title: Metal Compounds
1Metal Compounds
- Toxicity of Various Metal Compounds
2General Issues
- About 80 of the 105 elements in the periodic
table are regarded as metals fewer than 30 have
been reported to produce toxicity. - Metals are distributed naturally in the
environment by both geologic and biologic cycles. - A critical determinant of the metabolism and
toxic behavior of a metal is its biological
half-life. The half-life of cadmium and lead are
20 to 30 years whereas for metals such as
arsenic, cobalt, and chromium it is a few hours
to a few days.
3General Issues (Continued)
- Cellular targets for toxicity are specific
biochemical processes (enzymes) and/or membranes
of cells and organelles. - Alkyl compounds (organic compounds) are lipid
soluble and pass readily across biological
membranes, and they are only slowly dealkylated
to inorganic salts. Hence their excretion tends
to be slower than inorganic forms and the pattern
of toxicity tends to be different from inorganic
forms. - Ex. Methylmercury is primarily a neurotoxin
while mercuric chloride is toxic to the kidneys.
4General Issues (Continued)
- FACTORS INFLUENCING THE TOXICITY OF METALS
- Interactions with essential metals
- Formation of metal-protein complexes
- Age and stage of development
- Lifestyle factors
- Chemical form or speciation
- Immune status of host
5INDIVIDUAL METALS
6Three Forms of MercuryElemental, Inorganic,
Organic
- Hgo (elemental mercury)
- Hg (mercurous inorganic mercury)
- Hg (mercuric inorganic mercury)
- Methylmercury and dimethylmercury (organic forms)
7Global Sources and Distribution of Mercury
- The major natural source of mercury is the
natural degassing of the earths crust Volcanic
Activity. -
- Human Activity Source Fossil fuels (especially
coal) may contain as much as 1 ppm of mercury.
8Sources (Continued)
- Metallic mercury in the atmosphere represents the
major pathway of global transport of mercury.
Metallic mercury may be oxidized to mono or
divalent mercury in the presence of organic
matter. - Residence time of Hg vapor in the air is 0.4 to
3.0 years, global distribution. Hg is removed
from air by dry and wet deposition so therefore
it is deposited onto land and water by rain.
9Sources (Continued)
- Methylation of mercury is accomplished by
anaerobic bacteria in the aquatic environment.
10Toxicokinetics
- Metallic mercury volatilizes to mercury vapor and
most human exposure to metallic mercury is by
inhalation. This vapor is lipid soluble. - G.I. tract absorption of inorganic mercury salts
from food is low (7 15) whereas absorption of
methylmercury from G.I. tract is high (90 95).
11Toxicokinetics (Continued)
- The kidney contains the greatest of mercury
following exposure to inorganic mercury and
mercury vapor, whereas organic mercury has a
greater affinity for the brain. - Excretion is mainly by the biliary route with
enterohepatic recirculation in the case of
methylmercury.
12Toxicokinetics (Continued)
- Methylmercury, can cross the placenta to the
fetus and additional mercury exposure can occur
during nursing since methylmercury is also found
in milk at 5 of maternal blood. - Biological half-life is about 70 days for
methylmercury and about 40 days for inorganic
forms.
13Cellular Targets
- has a particular affinity for compounds
containing sulfhydryl groups - affects enzyme systems in microsomes and
mitochondria - becomes localized in lysosomes of kidney cells
14Toxicity
- Mercury vapor and methylmercury affect the CNS
-
- Inorganic mercury affects kidney
-
- Toxicity occurs at much lower levels in the fetus
than in adults.
15Mercury In Fish
- Methylmercury is produced both in the sediment
and in the water column by methylation of Hg by
microbes. - Fish obtain methylmercury from their diet and, to
a much lesser extent, from the water passed over
the gills. Diet accounts for 90 of uptake. - Assimilation efficiency for dietary uptake is 65
80 or greater. 7 12 assimilation
efficiency across gills.
16Mercury In Fish (Continued)
- Feeding habits and food-chain structure
influences methylmercury uptake in fish. - Get biomagnification of methylmercury
progressively increases from primary producers to
fish. Piscivorous fish have greater than
fish of lower trophic levels. Lake trout have a
greater of methylmercury when forage fish
are present versus invertebrates. - Fish from smaller, warmer lakes also have greater
s.
17Mercury In Fish (Continued)
- The of methylmercury in fish increases with
increasing age or size of fish. - Acidic bodies of water have greater methylmercury
production. - Fish from newly flooded reservoirs have high s
of methylmercury.
18Mercury In Fish (Continued)
- Nearly all of the mercury in fish is
methylmercury (95 99). - The greatest amount of mercury in the body of a
fish is found in the skeletal muscle even though
mercury is at a lower in skeletal muscle than
in brain.
19Mercury In Marine Mammals
- Marine mammals store the majority of mercury in
the inorganic forms because they have a very good
ability to demethylate organic mercury within
their bodies. - Transfer to fetus is low because only
methylmercury is able to cross the placenta.
20Human Exposure To Methlymercury
- Minamata Japan
- Iraq
- Seychelle Islands
21INDIVIDUAL METALS
22Forms of Arsenic
- Found as As3 or As5
- The most common As3 inorganic forms are arsenic
trioxide, sodium arsenite, and arsenic
trichloride. - The most common As5 inorganic forms are arsenic
pentoxide, lead arsenate, and calcium arsenate. - Organic forms may be 3 or 5 As and may occur as
methylated forms due to methylation by organisms
in soil, fresh water, and sea water.
23Forms (Continued)
- Trivalent forms of As are the principal toxic
forms. Pentavalent forms generally have little
or no effect. - However, 5 forms can be converted to 3 forms in
vivo.
24Toxicokinetics
- Exposure is through inhalation, drinking water,
and soil - Almost complete absorption from G.I. Tract
25Toxicokinetics (Continued)
- Excretion of inorganic forms is largly through
the urine. Methylated forms have a longer
half-life. Methylated forms seem to be a
detoxification product with dimethyl-As the
principal detox product. - As also has a predilection for skin and is
excreted by desquamation of skin and in sweat,
particularly during periods of profuse sweating.
26Toxicokinetics (Continued)
- Also concentrates in nails and hair.
- Human milk contains some As and As can be
transferred across the placenta ( in fetal
blood same as maternal blood).
27Cellular Targets
- Sulfhydryl-containing proteins and enzymes
systems are altered by exposure to As compounds. - Affects mitochondrial enzymes. Mitochondria
accumulate As. Succinic dehydrogenase activity
is inhibited and oxidative phosphorylation is
uncoupled. - As chelates with alpha-lipoic acid forming a
ring-like structure. Alpha-lipoic acid is an
essential cofactor for pyruvate dehydrogenase, an
enzyme required for energy production in the
Krebs Cycle.
28Cellular Targets (Continued)
- Some As forms mimic the phosphate anion in cells.
Substitution of As for phosphate would disrupt a
number of metabolic reactions that require
phosphorylation.
29Noncancer Effects
- Large doses (70 180 mg) can be fatal. Acute
effects sensory loss in peripheral nervous
system (degeneration of axons). - Chronic exposure to inorganic As leads to
neurotoxicity of both the peripheral and central
nervous systems. - Liver injury is also characteristic of chronic
exposure.
30Cancer Effects
- Skin cancer. Hyperpigmentation and
hyperkeratosis. Basal cell carcinoma and
squamous cell carcinomas. - Occupational exposure to airborne As may be
associated with lung cancer. The time period
between initiation of exposure and occurrence of
As-associated lung cancer is on the order of 34
to 45 years.
31Cancer Effects (Continued)
- Several studies suggest that As 3 compounds are
capable of producing chromosome breaks.
32Individual Metals
33General Issues
- Lead is the most ubiquitous metal
- Most susceptible populations are children,
particularly toddlers, infants in neonatal
period, and fetus - There is no demonstrated biological need for lead
34Intake of Lead
- Oral absorption
- Food
- Lead based indoor paint
- Contaminated drinking water
- Hand to mouth activity in children
- Lead-glazed pottery
- Inhalation absorption
- Lead dust from environmental sources
- Air from lead-containing industrial/auto emissions
35Intake of Lead (Continued)
- Dietary intake has decreased dramatically since
the 1940s (400 500 ug/day) to present (20
ug/day) in US. - Since the introduction of lead-free gasoline in
US, airborne exposure from auto exhaust in
minimal.
36Absorption
- Adults absorb 5 to 15 of ingested lead and
usually retain less than 5 of that absorbed - Children absorb 40 of ingested lead and retain
about 32 of that absorbed - About 90 of inhaled lead is small enough to be
retained in alveoli and get 100 absorption
37Distribution
- gt 90 of the Pb in the blood is in the red blood
cells (RBCs) - One compartment is the RBC membrane
- Second compartment is hemoglobin
- Redistribution of Pb from blood to skeleton with
half-life of 20 years - Pb crosses placenta to fetus to match levels in
maternal blood
38Toxicity of Lead
- Neurotoxicity
- Significant affect on timing of cell-to-cell
connections get modified neural circuits in
central nervous system - Demyelination and axon degeneration in peripheral
nervous system - Interference with synaptic transmissions Pb
substitutes for Ca at synapse
39Toxicity (Continued)
- Hematological Toxicity
- Anemia
- Fragile RBC membrane shortens RBC lifespan
- Impairment of heme synthesis
- Effects on myoglobin and CYP
- Myoglobin and CYPs also contain heme
40Heme Synthesis Inhibition
- Pb inhibits heme synthesis at several key points
in pathway - Aminolaevulinate synthetase
- Aminolaevulinate dehydrase
- Ferrochelatase
- Haem oxidase
- Coproporphyronogen oxidase
41Heme (Continued)
- Significant inhibition of amionolaevulinate
dehydrase is detectable in people with Pb blood
levels of 0.4 ug/ml, which results from normal
exposure to the urban environment.
42Toxicity (Continued)
- Renal Toxicity
- Acute exposure can cause reversible renal damage
- Chronic exposure causes permanent renal damage.
Get impaired ATP production in mitochondria of
proximal tube cells of nephron
43Toxicity (Continued)
- Organic Lead (tetraethyl Pb) is lipid soluble,
targets brain of developing fetus resulting in
Encephalophathy - Organic Lead does not effect heme synthesis or
kidney.
44Individual Metals
45General Issues
- Cadmium is a modern toxic metal industrial use
was minor until about 60 years ago - Use today is in electroplating, color pigments in
paints, batteries
46Absorption
- Airborne exposure in workplace
- Shellfish accumulate Cd from water
- Cigarette smoke
- Oral absorption is low
- Inhalation absorption is high
47Distribution
- In blood, binds to RBCs and to plasma proteins
(particularly albumin) - 50 to 75 of body burden is in liver and kidneys
- Half-life is 30 years
48Toxicity
- Pulmonary, Renal, and Bone Toxicity
- Damage to alveolar macrophages which release
enzymes that damage alveolar basement membranes
fibrosis - Cd-Metallothionein Renal toxicity
- Cd-Metallothionein Reproductive Protection
- Cd replaces Ca in bone Itai-Itai disease
49Toxicity (Continued)
- Carcinogen
- Lung cancer
- Testicular cancer
- Prostate cancer
50Individual Metals
51Toxicity of Tin Compounds
- Organic tin compounds are potent neurotoxins
- These compounds are often used as anti-fouling
paints on boats and ships - Compounds are also involved as endocrine
disrupting compounds
52Individual Metals
53General Issues
- Selenium is a required metal for humans at low
doses - Selenium can be toxic at high doses
- Embyotoxic and teratogenic to animals