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Biotransformation and Elimination of Toxicants Principles of Environmental Toxicology Instructor: Gregory Möller, Ph.D.. Principles of Environmental Toxicology 3 Learning Objectives, 2 •

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Biotransformation and Elimination

of Toxicants Principles of Environmental Toxicology

Instructor: Gregory Möller, Ph.D

University of Idaho

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, T½

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

Trang 2

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

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 NH2

R

S

R 2

R 1

R 1

R 2

C O

R2

R 1 C-O O

R 1

R 2

C S

RCH2OH

R 1

R 2

CH OH

S O

R 2

R 1

NHOH R

R 1 CH2OOH

RCHO

R 1

R 2

C O

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

NH2 HO

O

Glutathione

Trang 3

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

PII Cofactors: PAPS

OH O

O N

N

NH2

O

OH

P O O

OH

P OH

3’-Phosphoadenosine 5”-phosphosulfate

Principles of Environmental Toxicology

15

PII Cofactors: UDPGA

O

HO HO

H

H

H

H2C

H

N H

N O O

OH P O

O HO P O O O H

HO

H

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

GSH GST Toxic Epoxide

Phenol

Glucuronide

UDP-GT

Epoxide Hydratase

Dihydrodiol

Principles of Environmental Toxicology

17

Aniline

NH2

P450

H N

Principles of Environmental Toxicology

18

De-Alkylation

HC

O +

Phase II

Dimethyl-propyl-amine Methyl-propyl-amine Acetaldehyde

Trang 4

Free Radical Generation

C

Cl

Cl

NADH P450 Reducatase

C Cl

Cl Cl

Toxic Free Radical

GSH

Tetrachloro-methane

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

CoASH

H H

Sodium Fluoroacetate

Compound 1080

rodenticide

predator control

Principles of Environmental Toxicology

22

Fluorocitrate Metabolite

HO O

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

H2O

HO

O

O OH

O

HO

O

OH O

O HO

Aconitase

(Fluoro)Citrate

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

Trang 5

Aflatoxin B1 O

O

O

O

O

H

H

O

O

O

O

H

H

O

OH

B1

Q1 = hepatic metabolite

Aspergillus mycotoxin

found on corn, peanuts

and cottonseed

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

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

Trang 6

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)

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

Ureter

Bovine

Principles of Environmental Toxicology

36

Renal Filtration Microstructure

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Renal Histology

Tubules

Glomerulus

Microscopic

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 m2

Gray's Anatomy 1918

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