Tải bản đầy đủ (.pdf) (7 trang)

Biotransformation and Elimination of Toxicants pptx

Bạn đang xem bản rút gọn của tài liệu. Xem và tải ngay bản đầy đủ của tài liệu tại đây (326.42 KB, 7 trang )

1
Biotransformation and Elimination
of Toxicants
Principles of Environmental Toxicology
Instructor: Gregory Möller, Ph.D.
University of Idaho
Principles of Environmental Toxicology
2
Learning Objectives
• Explain the role of biotransformation in toxicokinetics.
• Describe how biotransformation facilitates elimination
of toxicants.
• Distinguish between Phase I
and Phase II reactions.
• Define bioactivation
or toxication.
Principles of Environmental Toxicology
3
Learning Objectives, 2
• Identify tissues and factors
involved in biotransformation.
• Summarize the role of elimination in
toxicokinetics.
• Describe processes occurring in
the kidney, liver and lung
related to the elimination
of toxicants.
Principles of Environmental Toxicology
4
Metabolism
• Sum of biochemical rxns occurring to a


molecule within the body.
– Anabolism - “build-up”
– Catabolism - “break-down”
• Occurs in the cytoplasm or
at specific organelles within
the cell.
• Storage affects the body’s
ability to biotransform and
eliminate.
– Bone, lipid.
Principles of Environmental Toxicology
5
Biotransformation
• Process that changes substances from hydrophobic
to hydrophilic to aid in elimination (grease to salt).
– Hydrophilic molecules are less able to cross cellular
membranes, hence fluid filterable (kidneys).
– Major elimination routes are
feces (biliary) and urine.
– Biological half-life, T
½
allows comparison of
rates of removal.
Principles of Environmental Toxicology
6
Biotransformation Reactions
• Grouped as Phase I (functional group modification)
and Phase II (conjugation).
• Goals
– Produce water soluble metabolites.

– Activate natural/endogenous compounds
for normal function.
• Some compounds undergo
bioactivation
.
– The biotransformed metabolite
is more toxic than the original
compound.
2
Principles of Environmental Toxicology
7
Results of Biotransformation
• Increase toxicity via a toxic metabolite.
• Decrease toxicity via metabolism of a toxic
parent compound.
• No effect on toxicity.
• Present to metabolize
endogenous compounds.
Principles of Environmental Toxicology
8
Major Categories/Reactions
Phase I
Phase II
Elimination
oxidation
reduction
hydrolysis
conjugation
synthesis
polar

very
polar
Principles of Environmental Toxicology
9
Enzymes of Biotransformation
• Oxidation (most important).
– Add O, remove H, increase valence.
– Cytochrome P-450, MFO, alcohol dehydrogenase,
oxidases, others.
• Reduction (less important).
– Remove O, add H, decrease valence.
– Reductases.
• Hydrolysis.
– Add water.
– Esterases, phosphtases, others.
Phase I Enzymes
Principles of Environmental Toxicology
10
Phase I Reactions
NH2R
S
R
2
R
1
R
1
R
2
C

O
R
2
R
1
C-O
O
R
1
R
2
CS
RCH2OH
R
1
R
2
CH
OH
SO
R
2
R
1
NHOHR
R
1
CH2OOH
RCHO
R

1
R
2
CO
R
2
HO
N-oxidation
S-oxidation
Carbonyl reduction
Ester Hydrolysis
Desulfuration
Dehydrogenation
+
Hughes
Principles of Environmental Toxicology
11
Enzymes of Biotransformation, 2
• Conjugation reactions.
• Enzymes (tranferases) + cofactor.
– Enzyme catalyzes.
– Cofactor donates group.
– Glucuronic acid, glutathione, sulfate,
acetyl group, methyl group.
– Tends to increase
molecular size and
polarity for excretion.
Phase II Enzymes
Principles of Environmental Toxicology
12

PII Cofactors: GSH
H
N
O
HS
O
N
H
NH
2
HO
O
OH
O
Glutathione
3
Principles of Environmental Toxicology
13
PII Cofactors: Acetyl-CoA
Acetyl Coenzyme A
N
N
N
NH
2
N
O
O
P
OH

O
O
O
P
O
HO
HO
O
NH
NH
O
S
HO
O
OH
P
HO
O
O
Principles of Environmental Toxicology
14
PII Cofactors: PAPS
OH
O
O
N
N
N
N
NH

2
OSO
O
OH
PO
O
OH
P
OH
OOH
3’-Phosphoadenosine
5”-phosphosulfate
Principles of Environmental Toxicology
15
PII Cofactors: UDPGA
O
HO
HO
H
H
H
H
2
C
H
N
H
N
O
O

OHP
O
O
HO
P
O
O
O
H
HO
H
HO
H
OH
H
H
-
O
O
Uridine-5’-
diphosphoglucuronic acid
Principles of Environmental Toxicology
16
Benzene Metabolism
OH
ST
O
OH
P450
PAPS

O
OSO
3
OH
OH
Glutathione
Epoxidation
G
SH
GST
Toxic Epoxide
Phenol
Glucuronide
UDP-GT
Epoxide
Hydratase
Dihydrodiol
Principles of Environmental Toxicology
17
Aniline
NH
2
P450
H
N
OH
Phase II
Amine
N-hydroxylation
Principles of Environmental Toxicology

18
De-Alkylation
N
P450
H
N
HC
O
+
Phase II
Dimethyl-propyl-amine
Methyl-propyl-amine
Acetaldehyde
4
Principles of Environmental Toxicology
19
Free Radical Generation
C
Cl
Cl
Cl Cl
N
A
DH
P450
Reducatase
C
Cl
Cl
Cl

To
x
ic F
r
ee Radical
GSH
Tet
r
achlo
r
o-methane
Principles of Environmental Toxicology
20
Case Study: Fluorocitrate and Kangaroos
• Fluorocitrate found in legume
pasture plants
of Western Australia.
– Gastrolobium and Oxylobium.
• Highly lethal (TD 1 mg/1080 kg).
– Leaf concentrations can be 2.6 g/kg.
• The rat and gray kangaroo
of Western Australia have
evolved resistance.
– In vivo defluorination w/ glutathione.
– Other kangaroos from areas
w/o these plants are not tolerant.
WACALM
Harborne
Principles of Environmental Toxicology
21

Rodenticide: Fluoroacetic Acid
OH
O
F
Co
A
SH
FCCOSCoA
H
H
Fluoroacetate Fluoroacetyl CoA
Sodium Fluoroacetate
Compound 1080
rodenticide
predator control
Principles of Environmental Toxicology
22
Fluorocitrate Metabolite
HO
O
OOH
O
AcCoA
FAcCoA
OH
HO
O
OH
O
O

HO
F
Principles of Environmental Toxicology
23
Krebs Cycle
OH
HO
O
OH
O
O
HO
F
AcCoA
FAcCoA
H
2
O
HO
O
OOH
O
HO
O
OH
O
O
HO
Aconitase
(Fluo

r
o)Cit
r
ate
Oxaloacetate
Cis-aconitate
Mitochondrial
energy production
Principles of Environmental Toxicology
24
Deoxynivalenol, Vomitoxin
O
HO
HO
O
O
O
HO
HO
OH
O
CH
2
OH
Fusarium trichothecene
mycotoxin found on
corn and barley
5
Principles of Environmental Toxicology
25

Aflatoxin B
1
O
O
O
O
O
H
H
O
O
O
O
O
O
H
H
O
OH
B
1
Q
1
= hepatic metabolite
Aspergillus mycotoxin
found on corn, peanuts
and cottonseed
Principles of Environmental Toxicology
26
Benzo[a]pyrene

OR
R = sulphate or glucuronic acid
• Polycyclic aromatic
hydrocarbon.
• Environmental carcinogen.
• Cell cultures from rodents,
fish and humans
Principles of Environmental Toxicology
27
Heavy Metal Toxicity - Pb
• Absorbed via Ca channels as divalent ion.
• Capable of reacting with a variety of binding sites.
– Protein precipitation.
• Specific toxic effect depends on rxns with ligands
that are essential for the living system.
• Metal ligands are formed with
sulfhydryl groups, as well as
amino, phosphate, imidazole,
and hydroxyl groups of enzymes
and essential proteins.
Principles of Environmental Toxicology
28
Heavy Metal Toxicity - Pb, 2
• Sensitivity of a system and degree of
interference determines clinical effects.
– Digestion/respiration → absorption.
–Liver → detoxication.
–Kidney → excretion.
• Antidotes are competing ligands.
N

NO
OH
O
OH
O
HO
O
HO
EDTA
Principles of Environmental Toxicology
29
Heavy Metal Toxicity - Pb, 3
• Metallic lead absorbed most efficiently
by the respiratory tract.
• 10% of ingested lead is absorbed.
– Small intestine.
– Lead salts are soluble in gastric juices; absorbed.
• Plasma to blood cells – erythrocytes.
• After oral ingestion:
– 60% bone (also hair, teeth).
– 25% liver (hepatocytes).
– 4% kidney (renal tubules).
– 3% intestinal wall.
Principles of Environmental Toxicology
30
Heavy Metal Toxicity - Pb, 4
• Some endpoints.
– Sulfhydral enzyme inhibition.
– K transport in RBC inhibited
• Anemia.

– Porphyrinuria.
• Excreted chiefly in
feces and urine.
• Chelating agents:
–Ca -EDTA.
– Penicillamine.
– Dimercaptrol (BAL).
C
H2
CH
C
H2
HO
SH
SH
2,3-Dimercapto-propan-1-ol
6
Principles of Environmental Toxicology
31
Case Study: Elevated PbB Associated with
Illicitly Distilled Alcohol, Alabama 1991
• The use of automobile radiators containing
lead-soldered parts in the illicit distillation of
alcohol (i.e., "moonshine") is an important
source of lead poisoning among persons in
some rural Alabama counties.
• In 1991, eight persons were diagnosed with
elevated blood lead levels (BLLs) at a local
hospital.
• 9 patients had been evaluated for alcohol-

related medical conditions at the hospital.
Manifestations included generalized tonic-clonic
seizures (six), microcytic anemia (five)
(hematocrit mean: 32.1%), encephalopathy
(two), upper extremity weakness (one), and
abdominal colic (one). BLLs ranged from 16
ug/dL to 259 ug/dL (median: 67 ug/dL).
MMWR (1992) 41(17);294-295
Principles of Environmental Toxicology
32
Case Study: “Moonshine” Lead Toxicity
• Seven patients required hospitalization for
48 hours or longer (range: 2-18 days). Three
of these received chelation therapy; initial
BLLs were 67, 228, and 259 ug/dL. One
patient, whose BLL was 67 ug/dL, died
during hospitalization from alcohol-
withdrawal syndrome complicated by
aspiration pneumonia.
• Patients reported moonshine ingestion
ranging from 0.2 L per day to 1.5 L per day.
• The lead contents of specimens of
moonshine confiscated from two radiator-
containing stills in the county in 1991 were
7400 ug/L and 9700 ug/L, compared with
nondetectable amounts (less than 1.0 ug/L)
in municipal water from the county.
• Consumption of 0.5 L per day of moonshine
containing 9700 ug/L lead would result in a
steady state BLL of approximately 190

ug/dL.
Principles of Environmental Toxicology
33
Elimination of Toxicants
• Urinary.
• Fecal.
• Respiratory.
• Other:
–Saliva.
–Sweat.
– Milk (transfer to child).
– Nails, Hair, Skin.
– Cerebrospinal fluid.
Hughes
Principles of Environmental Toxicology
34
Kidney
Principles of Environmental Toxicology
35
Renal Macrostructure
Renal cortex
Renal medula
Ureter
Bovine
Principles of Environmental Toxicology
36
Renal Filtration Microstructure
7
Principles of Environmental Toxicology
37

Renal Histology
Tubules
Glomerulus
Microscopic
Principles of Environmental Toxicology
38
Urinary Excretion
• Glomerular filtration
• Tubular secretion
• Tubular reabsorption
Principles of Environmental Toxicology
39
Fecal Excretion
• Excretion in bile to intestine.
– Active transport of toxicant parent and metabolites.
– Highly soluble Phase II metabolites (large, ionized)
• Excretion into the lumen of the GI tract.
– Direct diffusion from capillaries.
NLM
Principles of Environmental Toxicology
40
Exhaled Air
• Gas phase xenobiotics.
• Passive diffusion from blood
to alveolus via concentration
gradient.
– The total alveolar epithelial
surface area within an average
adult human lung has been
estimated to be as large as

100-140 m
2
.
Gray's Anatomy 1918

×