Pollution-Induced Germ-line Mutations in Gull and Mouse Tandem - - PowerPoint PPT Presentation

pollution induced germ line mutations in gull and mouse
SMART_READER_LITE
LIVE PREVIEW

Pollution-Induced Germ-line Mutations in Gull and Mouse Tandem - - PowerPoint PPT Presentation

Pollution-Induced Germ-line Mutations in Gull and Mouse Tandem Repeat DNA Dr. James S. Quinn Biology Department McMaster University DNA Damaging Agents In the Environment: - heritable mutations? Hamilton Harbour Remedial Action Plan:


slide-1
SLIDE 1

Pollution-Induced Germ-line Mutations in Gull and Mouse Tandem Repeat DNA

  • Dr. James S. Quinn

Biology Department McMaster University

slide-2
SLIDE 2

DNA Damaging Agents In the Environment:

  • heritable mutations?
slide-3
SLIDE 3

Hamilton Harbour Remedial Action Plan: Hamilton Harbour Remedial Action Plan: Hamilton Harbour Remedial Action Plan:

Designated area of concern under IJC in 1978 Remediation goals established for chemical and biological state of the area Our lab contributed with an attempt to establish a Method to monitor germ-line mutations

Heritable Mutations?

slide-4
SLIDE 4

Contaminants Can Damage DNA

body cells Mutation Cancer

Exposed

Sex cells Mutation

??

Unexposed offspring

slide-5
SLIDE 5

Outline

  • Germline mutation monitoring
  • Pollution and minisatellite mutations
  • Experimental studies of ESTR mutations in mice
  • Implications and reactions
  • What can be done and is often not done

(Hamilton’s legacy).

  • Future mutation work
slide-6
SLIDE 6

Contaminant-Induced Heritable Mutations: Difficult to study

  • Comparisons

between exposed and unexposed populations lack statistical power

  • Causal links

between exposure and mutation difficult to establish

  • Enormous sample

sizes and high treatment doses

  • Do not reflect

exposure under ambient conditions Natural Populations Laboratory Studies Few attempts have been made to study mutations induced under ambient environmental conditions

slide-7
SLIDE 7

Part 1: Germline mutation screening in herring gulls (Larus argentatus) on the Great Lakes

slide-8
SLIDE 8
slide-9
SLIDE 9
slide-10
SLIDE 10
slide-11
SLIDE 11
slide-12
SLIDE 12
slide-13
SLIDE 13
  • Dr. Carole Yauk
slide-14
SLIDE 14
slide-15
SLIDE 15

Mutation Detection:

  • Pedigree analysis
  • Multilocus DNA fingerprinting
  • Minisatellite loci
  • Non-parental bands = mutations

Minisatellite DNA:

  • Non-coding, repetitive DNA
  • High spontaneous mutation

rate

slide-16
SLIDE 16

Hamilton Harbour

Gulls Industrial core

slide-17
SLIDE 17

Germline Minisatellite Mutation Rates in Herring Gulls:

0.005 0.01 0.015 0.02 0.025 Hamilton Kent Island Presqu'ile Chantry Island

Per-band mutation rate Rural

Yauk and Quinn (1996) PNAS 93: 12137- 12141.

slide-18
SLIDE 18

Study Sites:

slide-19
SLIDE 19

Yauk, Fox, McCarry and Quinn, 2000. Mutation Research 452:211-218

slide-20
SLIDE 20

Mutation rate is negatively correlated with proximity to steel production:

0.5 1 1.5 2 2.5 Rural Urban 4 - 9km 2km 0km

P e r

  • b

a n d m u t a t i

  • n

r a t e x 1

Distance from steel mills

Yauk, Fox, McCarry and Quinn, 2000. Mutation Research 452:211-218

slide-21
SLIDE 21

Germline Mutation Screening: Herring Gulls

Germline minisatellite mutation rates elevated at sites with integrated steel mills Mutation rates negatively correlated with proximity to steel mills

(Yauk and Quinn 1996 PNAS, Yauk et al. 2000 Mutat Res.)

slide-22
SLIDE 22

?

slide-23
SLIDE 23

What is the Route of Mutagen Exposure?

Are Other Organisms at Risk?

slide-24
SLIDE 24

Germ-line mutation induction in other species

  • Elevated minisatellite mutation rates
  • humans living near Chernobyl and

in Kazakhstan

  • Elevated microsatellite mutation

rates - barn swallows living near Chernobyl

slide-25
SLIDE 25

Potential Difficulties in Interpreting Comparisons Among Natural Populations:

Underlying Genetics Isolating Route of Exposure Lifestyle / Behaviour Differences

slide-26
SLIDE 26

Development of mouse-specific repetitive DNA markers (ESTRs) :

  • Acute gamma irradiation (Dubrova et al.

1998, 2000)

  • PCBs and diesel exhaust (Hedenskog et
  • al. 1997)
  • ESTR markers more sensitive and efficient

than previous rodent tests (e.g., Specific locus test)

slide-27
SLIDE 27

Challenge: An experimental approach to detect heritable mutations caused by pollution.

Sentinel Animals, ambient conditions Sensitive ESTR markers in lab mouse studies

slide-28
SLIDE 28

Part 2: Germline mutation screening in sentinel rodents

slide-29
SLIDE 29
  • Dr. Chris Somers
slide-30
SLIDE 30

Airborne Emissions Contact Cooling

How Industrial By-Products Enter the Ecosystem in Hamilton Harbour:

Fall Out

slide-31
SLIDE 31

Hamilton Harbour

Gulls Industrial core Mice

slide-32
SLIDE 32
  • Adjacent to steel industry

and busy highway

  • Close to herring gull

nesting area

  • Long term air quality data

mouse shed

M.O.E.

Dofasco / Stelco

Pier 25 Exposure Site:

slide-33
SLIDE 33

Freelton Exposure Site:

  • ~30km north of Pier 25
  • Removed from known point

sources of pollution

  • Shed identical to one at

Pier 25

mouse shed

slide-34
SLIDE 34

Parents

1) Adults bred 6 weeks post-exposure

Offspring

2) Complete families sampled for comparative DNA Fingerprinting

slide-35
SLIDE 35

Mutation Detection: Pedigree DNA Profiling

P P 1 2 3 4 5 6

4.7kb 6.2kb 10.7kb 14.3kb

  • ESTR locus Ms6-hm

(GGGCA)n

  • Chromosome 4
  • Highly unstable in

germline

Mutations = changes in band size

slide-36
SLIDE 36

Overall inherited mutation rates:

0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 Rural Steel 0.00 0.01 0.02 0.03 0.04 0.05 0.06 0.07 0.08 Rural Steel

P e r

  • b

a n d m u t a t i

  • n

r a t e ( ± S E )

1.5X 2.0X Ms6-hm Hm-2 MMS10

Somers, Yauk, White, Parfett and Quinn. 2002. PNAS 99: 15904-15907

slide-37
SLIDE 37

Parental Origin of Mutations: Single locus ESTR markers

0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 0.40 Rural Steel Paternal Maternal

P e r

  • b

a n d m u t a t i

  • n

r a t e ( ± S E )

* Elevation in Hamilton mice is due mostly to mutations inherited through the paternal germline

Somers, Yauk, White, Parfett and Quinn. 2002. PNAS 99: 15904-15907

slide-38
SLIDE 38

Conclusions from Exp 1:

  • Ambient air at Steel site induced heritable

germ cell changes in exposed adult mice

  • Male germline more susceptible than female
slide-39
SLIDE 39

Next Steps?

  • Replication of the findings
  • Narrowing the field
slide-40
SLIDE 40

Protecting sentinel mice from particulate matter: HEPA filtration

Removes:

  • 99.99% > 0.3µm
  • 99.97% > 0.1µm

Ambient Air

slide-41
SLIDE 41

Two-way ANOVA (Env. Exposure per family, Paternal and maternal single locus ESTR rates)

0.2098 1.60 0.0004 13.79 1, 69

Interaction

0.7948 0.07 0.0060 8.03 1, 69

HEPA- filtration

0.0590 3.68 0.0090 7.22 1, 69

Exposure site P- value F- value P-value F-value df Source

Maternal Paternal

slide-42
SLIDE 42

Overall germline mutation rates:

0.00 0.05 0.10 0.15 0.20 0.25 0.30 Rural Rural HEPA Rural male Steel Steel HEPA Steel male 0.00 0.01 0.01 0.02 0.02 0.03 0.03 0.04 0.04 0.05 Rural Rural HEPA Rural male Steel Steel HEPA Steel male

Per-band mutation rate (±SE)

Ms6-hm Hm-2 MMS10

Somers, McCarry, Malek, and Quinn. 2004. Science 304: 1008-1010

slide-43
SLIDE 43

Paternal and Maternal Mutation Rates

0.00 0.05 0.10 0.15 0.20 0.25 0.30 0.35 0.40 Rural Rural HEPA Rural male Steel Steel HEPA Steel male Paternal Maternal

P e r

  • b

a n d m u t a t i

  • n

r a t e ( ± S E )

Paternal germline significantly affected

Somers, McCarry, Malek, and Quinn. 2004. Science 304: 1008-1010

slide-44
SLIDE 44

Pier 25 Pier 25 Pier 25 Freelton Freelton Freelton

0.02 0.04 0.06 0.08 0.1 0.12 Pier 25 Freelton

Mean Daily TSP (g)

High High High-

  • volume air sampling: 24 hour period

volume air sampling: 24 hour period volume air sampling: 24 hour period

slide-45
SLIDE 45

What might be causing mutations?

50 100 150 200 1994 1995 1996 1997 1998 1999

Total PAH conc. (ng/m3)

Exposure year 117.6 ng/m3

PAHs from coal combustion are a good candidate group

slide-46
SLIDE 46

Air chemistry: PAH testing

*Pyrene Benzo[a]fluorene Benzo[b]fluorene Benzo[b]naphtho[2,1-d]thiophene Benzo[ghi]fluoranthene Benzo[c]phenanthrene Benzo[b]naphtho[2,3-d]thiophene Benz[a]anthracene Cyclopenta[cd]pyrene *Chrysene Benzanthrone Benz[a]anthracene-7,12 dione Benzo[b]fluoranthene Benzo[k]fluoranthene Benzo[j]fluoranthene *Benzo[e]pyrene *Benzo[a]pyrene *Perylene Indeno[1,2,3-cd]pyrene *Dibenz[a,c]anthracene Picene Benzo[ghi]perylene *Coronene Dibenzo[a,e]pyrene Dibenzo[a,i]pyrene Dibenzo[a,h]pyrene

slide-47
SLIDE 47

Total PAHs: TSP

5 10 15 20 25 30 1 to 3 4 to 9 10 to 18 19 to 23 24

Rural Steel

PAH concentration (ng/m3) Daily hours downwind of industrial core

4x 3x 10x 40x 75x 171x Weighted average: 33-fold difference between sites; Rural = 0.4ng/m3, steel = 13.4ng/m3

slide-48
SLIDE 48

Implications?

slide-49
SLIDE 49

Possible Human Health Risks to the unborn

  • Genetic diseases influenced by tandem repeat DNA:
  • Cancers associated with Hras oncogene
  • Type I Diabetes
  • Type of Epilepsy
  • Huntington’s disease
  • Fragile X syndrome
  • Possible Changes in “coding” genes (requires demonstration

that ESTR assay reflects similar changes in genes)

slide-50
SLIDE 50

Around your home

slide-51
SLIDE 51

Around Your City

  • Leaves filter particulate air

pollution

  • Protect forests, plant trees
  • Limit road construction

and urban sprawl

  • Walk, bike, bus, or car pool
slide-52
SLIDE 52

Around your city/province/country

slide-53
SLIDE 53
slide-54
SLIDE 54
slide-55
SLIDE 55
slide-56
SLIDE 56

0.2098 1.60 0.0004 13.79 1, 69

Interaction

0.7948 0.07 0.0060 8.03 1, 69

HEPA- filtration

0.0590 3.68 0.0090 7.22 1, 69

Exposure site P- value F- value P-value F-value df Source

Maternal Paternal

Parental investment in Gametes? Timing?

slide-57
SLIDE 57

Future Research (collaboration with Carole Yauk and others)

  • In utero exposures – maternal mutations
  • Stability of mutations to F2
  • DNA expression in exposed individuals

– protection of germ-line DNA

  • Possible genomic instability
slide-58
SLIDE 58

Exposure through pregnancy to birth Non-exposed male Non-exposed male Score pedigree mutation to determine mutation rates in oocytes Score mutation in sperm using SM-PCR

slide-59
SLIDE 59

Conclusions:

  • Urban/Industrial air pollution induces germline

mutations in tandem repeat DNA

  • Males more sensitive than females
  • HEPA filtration reduces mutation induction
  • Airborne particles play major role in mutation

induction

slide-60
SLIDE 60

Acknowledgements

  • Dr. Carole Yauk
  • Dr. Chris Somers
  • ECOWISE (Tri-Council Green

Plan)

  • National Cancer Institute of

Canada

  • Wildlife Toxicology Fund
  • Toxic Substance Research

Initiative

  • NSERC
  • Environment Canada
  • Health Canada
  • Dr. Bradley White
  • Dr. Brian McCarry
  • Numerous Field and

Laboratory Research Assistants

  • Co-operative Landowners