an interspecies comparison of toxicity pathways mediating

35
AN INTERSPECIES COMPARISON OF TOXICITY PATHWAYS MEDIATING NEURODEVELOPMENTAL TOXICITY IN NEUROSPHERES - AND NOVEL COMPUTATIONAL APPROACHES FOR HIGH CONTENT IMAGE ANALYSES (HCA) Ellen Fritsche EPA’s Computational Toxicology Communities of Practice September 25 th 2014

Upload: vantuyen

Post on 05-Jan-2017

224 views

Category:

Documents


2 download

TRANSCRIPT

Page 1: an interspecies comparison of toxicity pathways mediating

AN INTERSPECIES COMPARISON OF TOXICITY PATHWAYS MEDIATING NEURODEVELOPMENTAL TOXICITY IN NEUROSPHERES - AND NOVEL COMPUTATIONAL APPROACHES FOR HIGH CONTENT IMAGE ANALYSES (HCA)

Ellen Fritsche EPA’s Computational Toxicology Communities of Practice September 25th 2014

Page 2: an interspecies comparison of toxicity pathways mediating

Cell  Biological  Processes  performed  by  NPC  

With courtesy from William Mundy, U.S. Environmental Protection Agency and John Havel, SRA International, Inc.

Page 3: an interspecies comparison of toxicity pathways mediating

Epi-genetics

Page 4: an interspecies comparison of toxicity pathways mediating

The  Neurosphere  Method  

Fetal Brain Culture as Neurospheres

NPC Proliferation: -Increase in size/time -BrdU incorporation

NPC Differentiation: -Neurons -Astrocytes -Oligodendrocytes

NPC Migration: -Total migration distance -number of migrated cells -neuronal migration

Neural Stem/Progenitor Cells (NPCs, Lonza)

Fetal Brain

Neural Stem/Progenitor Cells self-prepared

Page 5: an interspecies comparison of toxicity pathways mediating

From Breier…Fritsche.. et al. Neurotoxicol Teratol 2009

     The  ‘Neurosphere-­‐Assay’  

Apoptosis

BrdU

Fritsche et al. Environ Health Perspect 2005

Moors et al. Toxicol Appl Pharmacol 2007

Moors et al. Environ Health Perspect 2009

Moors et al. Genes & Immunity 2010

Tegenge et al. Cell. Mol. Life Sci. 2010

Schreiber et al. Environ Health Perspect 2010

Gassmann et al. Environ Health Perspect 2010

Verner et al. Toxicol in Vitro 2011

Fritsche et al. Methods Mol Biol 2011

Gassmann et al. Toxicol in Vitro 2012

Bal-Price et al. ALTEX 2012

Baumann et al. Curr. Protoc. Toxicol. 2014

Gassmann et al. Arch. Toxicol. 2014

Fritsche Methods Pharmacol. Toxicol. 2014

Alépée et al. ALTEX 2014

3 days

5 days

Page 6: an interspecies comparison of toxicity pathways mediating

Outline  

•  Thyroid Hormone (TH)

•  Arylhydrocarbon Receptor (AhR)

•  Valproic Acid

-  Histone Deacetylase (HDAC) inhibition

-  Apoptosis

•  HCA (Cellomics Arrayscan & self-written

algorithms ‘Omnisphero’)

Page 7: an interspecies comparison of toxicity pathways mediating

Thyroid  Hormone  

E11-­‐E14  =  

GW  6-­‐9  P1-­‐7  =  

GW  18-­‐30   P8-­‐14  =  

GW  32-­‐40  

Perez-Castillo et al, Endocrinology 117:2457-2461,1985

Ontogeny of T3 receptors in rat

T H R a1 e x p re s s io nC

op

y n

um

be

rs o

f T

HRa

1/

10

00

0 ß

Ac

tin

P r o l 2 4 h D iff0

5 0

1 0 04 0 0

6 0 0

8 0 0

1 0 0 0h N P C (n = 3 )

m N P C (n = 3 )

α1 α

1 T H R b1 e x p re s s io n

Co

py

nu

mb

ers

of

TH

Rb

1/

10

00

0 ß

Ac

tin

P r o l 2 4 h D iff0

5

1 0

1 5

2 0h N P C (n = 3 )

m N P C (n = 3 )

β

β

www.translatingtime.net

Page 8: an interspecies comparison of toxicity pathways mediating

Thyroid  Hormone  

O4

+ c

ell

s [

% c

on

tro

l]

C T 3 T 4 T 3 T 40

5 0

1 0 0

1 5 0

2 0 0

*

O lig o d e n d ro g e n e s isH a ir le s s e x p re s s io n

Co

py

nu

mb

ers

of

Ha

irle

ss

/10

00

0 ß

Ac

tin

C 3 n M T 30

5 0

1 0 0

1 5 0

2 0 0

2 5 0h N P C

m N P C

*

*

O lig o d e n d ro g e n e s is o f T H R b- /- m N P C s

O4

+ c

ell

s [

% c

on

tro

l]

0

5 0

1 0 0

1 5 0

2 0 0W ild ty p e (n = 4 )

T H R b- /- (n = 1 )

1 0 µM B D E -9 9

3 n M T 3

-

-

+

-

-

+

+

+

*

*

β

β

O lig o d e n d ro g e n e s is o f T H R a- /- m N P C s

O4

+ c

ell

s [

% c

on

tro

l]

0

5 0

1 0 0

1 5 0

2 0 0 W ild ty p e (n = 4 )

T H R a - /- (n = 2 )

1 0 µM B D E -9 9

3 n M T 3

-

-

+

-

-

+

+

+

*

*

α

α

H u m a n o lig o d e n d ro g e n e s is

O4

+ c

ell

s [

% c

on

tro

l]

0

5 0

1 0 0

1 5 0

2 0 0

2 µM B D E -9 9

3 n M T 3

-

-

+

-

-

+

+

+

* *

O4 Hoechst

Transgenic animals kindly provided by Heike Heuer, IUF

Page 9: an interspecies comparison of toxicity pathways mediating

Thyroid  Hormone  

BDE-99

T3 OL formation

OL maturation

THRα

BDE-99

M O G e x p re s s io n - m N P C

DD

CT

[no

rme

d t

o C

of

da

y 1

]

0

5

1 0

P ro life ra tin g

1 d d iffe re n tia t in g

3 d d iffe re n tia t in g

5 d d iffe re n tia t in g

1 0 µM B D E -9 9

3 n M T 3

-

-

+

-

-

+

+

+

M B P e x p re s s io n - h N P C

DD

CT

[no

rme

d t

o C

of

da

y 1

]

02468

1 0

2 02 53 03 54 0 P ro life ra tin g

1 d d iffe re n tia t in g

3 d d iffe re n tia t in g

5 d d iffe re n tia t in g

2 µM B D E -9 9

3 n M T 3

-

-

+

-

-

+

+

+

*

#

IC50 = 14 µM

Page 10: an interspecies comparison of toxicity pathways mediating

BDE-99

T3 OL formation

OL maturation

THRα

BDE-99

X

M O G e x p re s s io n - m N P C

DD

CT

[no

rme

d t

o C

of

da

y 1

]

0

5

1 0

P ro life ra tin g

1 d d iffe re n tia t in g

3 d d iffe re n tia t in g

5 d d iffe re n tia t in g

1 0 µM B D E -9 9

3 n M T 3

-

-

+

-

-

+

+

+

M B P e x p re s s io n - h N P C

DD

CT

[no

rme

d t

o C

of

da

y 1

]

02468

1 0

2 02 53 03 54 0 P ro life ra tin g

1 d d iffe re n tia t in g

3 d d iffe re n tia t in g

5 d d iffe re n tia t in g

2 µM B D E -9 9

3 n M T 3

-

-

+

-

-

+

+

+

*

#

Thyroid  Hormone  

IC50 = 2 µM

Page 11: an interspecies comparison of toxicity pathways mediating

Gassmann et al. Environ Health Perspect 2010

1 10 10 0.1 1 0.750

25

50

75

100

125

*

µM3-MC Bap MNF MeHgClDMSO

% m

igra

tio

n

AhR    Agonists  

AhR    Antagonist   AhR    

Agonists  AhR    

Antagonist  

AhR  -­‐  migraOon  

Gassmann et al.

1574 VOLUME 118 | NUMBER 11 | November 2010 Environmental Health Perspectives

by 3-MC or B(a)P (Figure 2D). Interestingly, TCDD did not disrupt wild-type mNPC migration despite AhR activation (Figure 2D). This might be due to the fact that, in con-trast to 3-MC and B(a)P, TCDD is hardly metabolized and thus does not produce reactive intermediates.

AhR-dependent gene transcription. AhR-dependent gene transcription is inducible only in mNPCs, and not in hNPCs because of low abundance of AhR and ARNT tran-scripts and absence of AhR protein in human cells. Because 3-MC, B(a)P, and MNF did not influence hNPC viability, proliferation,

or migration but did modulate proliferation or migration of mNPCs, we determined AhR and ARNT mRNA expression after exposure to these compounds in hNPCs and mNPCs under proliferating and di!erentiating condi-tions. AhR and ARNT mRNAs were expressed at very low copy numbers in hNPCs (0.6–2.5 and 13/1,000 copies -actin, respectively) and higher copy numbers in mNPCs (20–63 and 716–1,045/1,000 copies -actin, respec-tively) (Table 1). In addition, CYP1A1 expres-sion was undetectable in untreated hNPCs. That -actin was in this case valid to use as a house keeping gene was demonstrated by

normalization of proliferating versus differ-entiating NPCs to three additional house-keeping genes [RPL27, RPL30, OAZ1; see Supplemental Material, Figure 2 (doi:10.1289/ehp.0901545)]. Expression of the AhR target genes AhRR, CYP1A1, CYP1B1, and c-myc was not significantly induced by 10 µM 3-MC after 6, 12, 24, and 48 hr of di!erentiation in hNPCs (Figure 3A). We obtained comparable results for hNPCs from a second individual after 6 hr of treatment (data not shown). In contrast, 6 hr of exposure to 10 µM 3-MC significantly induced Cyp1a1 and Cyp1b1 mRNA in wild-type mNPCs to levels 6.6 ± 1.7 and 2.5 ± 0.25 times higher than con-trols, respectively (Figure 3C). Although 1 nM TCDD did not disturb neural migration, it induced AhR signaling in wild-type mNPCs, increasing Cyp1a1 expression 21 times relative to controls (Figure 3C, inset).

Comparison of mRNA expression lev-els between hNPCs and mNPCs showed that genes belonging to the AhR machin-ery and AhR-dependent genes were gener-ally expressed in higher copy numbers/1,000 copies -actin in mNPCs than in hNPCs (Table 1). Lack of AhR protein in hNPCs was confirmed by Western blot (Figure 3B). "ese results demonstrate that AhR signaling pathway gene products mediate the e!ects of the AhR agonists 3-MC and B(a)P and the AhR antagonist MNF on proliferation and migration in mNPCs, because AhR-deficient mNPCs are protected against these effects (Figure 3C, inset).

Discussion"e development of cell-based, non animal test-ing strategies for hazard assessment of chemicals is currently one of the most important tasks in toxicological research. In this regard, it is most important to choose appropriate model systems that are truly predictive for humans (Krewski et al. 2009; National Research Council 2007). Human tumor cell lines that are easily acces-sible in large quantities bear the restriction that they do not represent cellular metabolism and signal transduction of normal cells. In con-trast, primary cells are often obtained as ex vivo cultures from rodents. Such primary cultures are regarded as superior to tumor-derived cells. However, species-specific differences limit their application. One example of how rodent primary cells can indeed mis classify hazards for humans is provided by this study, which shows mouse-derived primary cells to be more susceptible to AhR modulation than their human counter parts. With regard to chemical testing, it is critical to be aware of such di!erences in order to avoid over- or under estimating hazards that chemicals pose to humans, and thereby protect human health and allow industry production and develop-ment of chemicals at the same time.

Figure 2. AhR agonists shorten wild-type mNPC but not hNPC migration. hNPCs (A and C) and wild-type (B and D) and AhR-KO (D) mNPCs were exposed to 3-MC, B(a)P, TCDD, MNF, or MeHgCl (PC) during differen-tiation for 48 hr. Migration distance from the edge of the sphere to the furthest outgrowth was measured. Data represent means ± SEs of two (AhR-KO) to five independent experiments (5–8 spheres/exposure). Bar = 500 μm. *p < 0.05 compared with 0.1% DMSO.

125

100

75

50

25

0

125

100

75

50

25

0

Mig

ratio

n (%

)

Mig

ratio

n (%

)

*

*

**

*

13-MC TCDD

DMSO

WT AhR-KO

Treatment (µM) Treatment (µM)

MNF MeHgCI MeHgCIDMSO

3-MC MNF10 10 10 100.001 0.0010.1 0.11 1 1 11

Human

Human

Mouse

Mouse

B(a)PTCDDB(a)P

Table 1. Comparison of human and mouse mRNA copy numbers/1,000 copies of -actin in proliferating and 24-hr differentiating NPCs.a

Human Mouse Mouse:human ratioGene Prolif Diff Prolif Diff Prolif DiffAhR 2.45 0.62 20.08 63.21 8.19 102.12ARNT 12.95 13.55 716.26 1045.07 55.31 77.13AhRR 0.94 0.61 79.21 387.55 84.24 638.85CYP1A1 < 0.001 < 0.001 18.63 31.64 ND NDCYP1B1 0.01 0.06 146.24 834.91 16407.23 14990.75C-MYC 5559.59 3017.13 14835.55 15967.72 2.67 5.29Abbreviations: Diff, differentiating; ND, not detectable; Prolif, proliferating.aData represent at least three independent experiments. The mouse:human ratio is shown to compare human and mouse mRNA expression levels.

Gassmann et al.

1574 VOLUME 118 | NUMBER 11 | November 2010 Environmental Health Perspectives

by 3-MC or B(a)P (Figure 2D). Interestingly, TCDD did not disrupt wild-type mNPC migration despite AhR activation (Figure 2D). This might be due to the fact that, in con-trast to 3-MC and B(a)P, TCDD is hardly metabolized and thus does not produce reactive intermediates.

AhR-dependent gene transcription. AhR-dependent gene transcription is inducible only in mNPCs, and not in hNPCs because of low abundance of AhR and ARNT tran-scripts and absence of AhR protein in human cells. Because 3-MC, B(a)P, and MNF did not influence hNPC viability, proliferation,

or migration but did modulate proliferation or migration of mNPCs, we determined AhR and ARNT mRNA expression after exposure to these compounds in hNPCs and mNPCs under proliferating and di!erentiating condi-tions. AhR and ARNT mRNAs were expressed at very low copy numbers in hNPCs (0.6–2.5 and 13/1,000 copies -actin, respectively) and higher copy numbers in mNPCs (20–63 and 716–1,045/1,000 copies -actin, respec-tively) (Table 1). In addition, CYP1A1 expres-sion was undetectable in untreated hNPCs. That -actin was in this case valid to use as a house keeping gene was demonstrated by

normalization of proliferating versus differ-entiating NPCs to three additional house-keeping genes [RPL27, RPL30, OAZ1; see Supplemental Material, Figure 2 (doi:10.1289/ehp.0901545)]. Expression of the AhR target genes AhRR, CYP1A1, CYP1B1, and c-myc was not significantly induced by 10 µM 3-MC after 6, 12, 24, and 48 hr of di!erentiation in hNPCs (Figure 3A). We obtained comparable results for hNPCs from a second individual after 6 hr of treatment (data not shown). In contrast, 6 hr of exposure to 10 µM 3-MC significantly induced Cyp1a1 and Cyp1b1 mRNA in wild-type mNPCs to levels 6.6 ± 1.7 and 2.5 ± 0.25 times higher than con-trols, respectively (Figure 3C). Although 1 nM TCDD did not disturb neural migration, it induced AhR signaling in wild-type mNPCs, increasing Cyp1a1 expression 21 times relative to controls (Figure 3C, inset).

Comparison of mRNA expression lev-els between hNPCs and mNPCs showed that genes belonging to the AhR machin-ery and AhR-dependent genes were gener-ally expressed in higher copy numbers/1,000 copies -actin in mNPCs than in hNPCs (Table 1). Lack of AhR protein in hNPCs was confirmed by Western blot (Figure 3B). "ese results demonstrate that AhR signaling pathway gene products mediate the e!ects of the AhR agonists 3-MC and B(a)P and the AhR antagonist MNF on proliferation and migration in mNPCs, because AhR-deficient mNPCs are protected against these effects (Figure 3C, inset).

Discussion"e development of cell-based, non animal test-ing strategies for hazard assessment of chemicals is currently one of the most important tasks in toxicological research. In this regard, it is most important to choose appropriate model systems that are truly predictive for humans (Krewski et al. 2009; National Research Council 2007). Human tumor cell lines that are easily acces-sible in large quantities bear the restriction that they do not represent cellular metabolism and signal transduction of normal cells. In con-trast, primary cells are often obtained as ex vivo cultures from rodents. Such primary cultures are regarded as superior to tumor-derived cells. However, species-specific differences limit their application. One example of how rodent primary cells can indeed mis classify hazards for humans is provided by this study, which shows mouse-derived primary cells to be more susceptible to AhR modulation than their human counter parts. With regard to chemical testing, it is critical to be aware of such di!erences in order to avoid over- or under estimating hazards that chemicals pose to humans, and thereby protect human health and allow industry production and develop-ment of chemicals at the same time.

Figure 2. AhR agonists shorten wild-type mNPC but not hNPC migration. hNPCs (A and C) and wild-type (B and D) and AhR-KO (D) mNPCs were exposed to 3-MC, B(a)P, TCDD, MNF, or MeHgCl (PC) during differen-tiation for 48 hr. Migration distance from the edge of the sphere to the furthest outgrowth was measured. Data represent means ± SEs of two (AhR-KO) to five independent experiments (5–8 spheres/exposure). Bar = 500 μm. *p < 0.05 compared with 0.1% DMSO.

125

100

75

50

25

0

125

100

75

50

25

0

Mig

ratio

n (%

)

Mig

ratio

n (%

)

*

*

**

*

13-MC TCDD

DMSO

WT AhR-KO

Treatment (µM) Treatment (µM)

MNF MeHgCI MeHgCIDMSO

3-MC MNF10 10 10 100.001 0.0010.1 0.11 1 1 11

Human

Human

Mouse

Mou

se

B(a)PTCDDB(a)P

Table 1. Comparison of human and mouse mRNA copy numbers/1,000 copies of -actin in proliferating and 24-hr differentiating NPCs.a

Human Mouse Mouse:human ratioGene Prolif Diff Prolif Diff Prolif DiffAhR 2.45 0.62 20.08 63.21 8.19 102.12ARNT 12.95 13.55 716.26 1045.07 55.31 77.13AhRR 0.94 0.61 79.21 387.55 84.24 638.85CYP1A1 < 0.001 < 0.001 18.63 31.64 ND NDCYP1B1 0.01 0.06 146.24 834.91 16407.23 14990.75C-MYC 5559.59 3017.13 14835.55 15967.72 2.67 5.29Abbreviations: Diff, differentiating; ND, not detectable; Prolif, proliferating.aData represent at least three independent experiments. The mouse:human ratio is shown to compare human and mouse mRNA expression levels.

Page 12: an interspecies comparison of toxicity pathways mediating

1"

10"

100"

1000"

10000"

100000"

1000000"

AhR" ARNT" CYP1A1" CYP1B1"

*

*

mRNA

Gassmann  et  al.  Environ  Health  Perspect  2010  

7  x  

3  x  

What  is  the  reason  for  species-­‐specific  differences?  

Gassmann et al. Environ Health Perspect 2010

hNPC  

/105

co

pie

s β-

Act

in

3-­‐MC  DMSO  

human   mouse  

HepG2  

GAPDH

AhR

Protein

AhR  -­‐  gene/protein  expression  

Human NPC are protected against AhR-dependent toxicity of PAH due to lack of AhR expression

Page 13: an interspecies comparison of toxicity pathways mediating

?

Valproic  Acid  

↑ ↑

↓ Molecular  mechanisms:  Prolifera>on:  wnt  –  β-­‐catenin  (Fo>  et  al.  2013)  Apoptosis:  Bcl-­‐2  expression  (Go  et  al.  2011)  Differen>a>on:  suggested  indirectly  by  increasing  the  NPC  pool?  HDAC  inhibi>on  suggested  (Montgomery  et  al.  2004)  

? ↑

Apoptosis:  Bcl-­‐2  expression  (Go  et  al.  2011)  

Apoptosis

Apoptosis

E11-­‐E14  =  

GW  6-­‐9  P1-­‐7  =  

GW  18-­‐30   P8-­‐14  =  

GW  32-­‐40  

↓ Fo>  et  al.  2013  

↑ Apoptosis

Yochum  et  al.  2011  

Mech.:  HDAC  inhibi>on  

Page 14: an interspecies comparison of toxicity pathways mediating

Valproic  Acid  -­‐  NPC  proliferaOon  

NPC proliferation

RAT

HUMAN

Baumann et al. in preparation

IC50 = 380 µM

IC50 = 756 µM

Page 15: an interspecies comparison of toxicity pathways mediating

Valproic  Acid-­‐  NPC  differenOaOon  

NPC differentiation RAT

HUMAN

Baumann et al. in preparation

IC50 = 321 µM

IC50 = 3177 µM

Page 16: an interspecies comparison of toxicity pathways mediating

Valproic  Acid  

↑ ↑

↓ ↓ ↑ Apoptosis

Apoptosis

E11-­‐E14  =  

GW  6-­‐9  P1-­‐7  =  

GW  18-­‐30   P8-­‐14  =  

GW  32-­‐40  

↓ ↓

↑ Apoptosis

•  NPC  prolifera>on  is  inhibited  by  VPA-­‐dependent  HDAC  inhibi>on  (Baumann  et  al.  in  prep)  

•  VPA  does  not  inhibit  neuronal  differen>a>on  of  rat  NPC,  but  induces  neuronal  apoptosis  due  to  forma>on  of  ROS.  

•  Human  neurons  are  protected  against  VPA-­‐induced  apoptosis.    

Page 17: an interspecies comparison of toxicity pathways mediating

Long-Term Culture (25d) of hNPCs in Mal-PVA Hydrogels (Cellendis) (Hellwig et al. in preparation)

200 x mag. 200 x mag. Phalloidin, Hoechst, ß-III tubulin

Page 18: an interspecies comparison of toxicity pathways mediating

Summary  (I)  

•  Primary Neurospheres seem to conserve NPC molecular signatures and functions ex vivo into in vitro.

•  Due to the multiple neurodevelopmental processes neurospheres are apt to mimic in vitro, they are well suited for investigations ‘from pathway to function’.

•  A variety of interspecies differences in NPC signaling seem to exist between human and rodent NPCs.

•  Studying the molecular similarities/differences of neurospheres will contribute to human risk assessment for DNT, especially in the context of the ‘Adverse Outcome Pathway’ concept.

Page 19: an interspecies comparison of toxicity pathways mediating

HCA  in  differenOaOng  NPC  

Ø  Information on the whole migration area, not just random areas of a well.

Ø  Software needs to distinguish between different cell types.

Ø  Issue of a high density culture needs to be overcome and neurons correctly identified.

Ø  Varying densities in different areas around sphere core.

196x

Page 20: an interspecies comparison of toxicity pathways mediating

From: Breier et al., Toxicological Science, 2008 Harrill et al., Neuro Toxicology, 2010 Harrill et al., Toxicology in vitro, 2011

Synaptogenesis

Proliferation/ Viability

Neurite Outgrowth

High  Content  Image  Analyses  (HCA)  for  DNT  tesOng    

Page 21: an interspecies comparison of toxicity pathways mediating

HCA  in  differenOaOng  NPC  

Neuronal Quantification

Neuronal Morphology

Migration

Neuronal Positioning

Neuron/Nuclei Identification

Schmuck et al. in preparation

Page 22: an interspecies comparison of toxicity pathways mediating

Thresholding (Isodata) Watershade

Thresholding (Isodata)

Raw images Binary images

Omnisphero:  Image  Pre-­‐processing  

Schmuck et al. in preparation

Page 23: an interspecies comparison of toxicity pathways mediating

Optional: Manual annotation Composite Fill Neuron Tracer

Schmuck et al. in preparation

Omnisphero:  Neuron  IdenOficaOon  

Page 24: an interspecies comparison of toxicity pathways mediating

Omnisphero:  Automated  Analyses  

Schmuck et al. in preparation

Page 25: an interspecies comparison of toxicity pathways mediating

EC50-Values EGF [ng/ml]

Acrylamide [mM]

MeHgCl [µM]

Manual 0,96 0,30 0,045

Neuronal Profiling 1,442 0,34 0,049

Composite Fill 0,67 0,31 0,104

Neuron Tracer 1,022 0,41 0,051

Neurogenesis:  comparison  of  methods  (IC50  values)  

Acrylamide EGF Methylmercury

Schmuck et al. in preparation

Page 26: an interspecies comparison of toxicity pathways mediating

Neurogenesis:  Accuracy  &  Precision  

Acrylamide EGF Methylmercury

Detection Power (DP)

False-Positives (FP)

Schmuck et al. in preparation

Page 27: an interspecies comparison of toxicity pathways mediating

Neurite  outgrowth:  Accuracy  &  Precision  

Schmuck et al. in preparation

Page 28: an interspecies comparison of toxicity pathways mediating

Floodfill-Filter

Program written by Thomas Temme

Sphere-­‐specific  Endpoints  

Page 29: an interspecies comparison of toxicity pathways mediating

Sphere-­‐specific  Endpoints:  MigraOon  distance  

Page 30: an interspecies comparison of toxicity pathways mediating

∑= n

n

n

n

n

n

Nuclein

NeuronsnNuclein

Neuronsn

1 )()(

)()(

σ

R in g n u m b e r

Ne

uro

n D

en

sit

y

1 2 3 4 5 6 7 8 90 .0

0 .5

1 .0

1 .5

2 .0

Neuronal  Density  DistribuOon  

Page 31: an interspecies comparison of toxicity pathways mediating

BrainSpan: Atlas of the Developing Human Brain [Internet]. Funded by ARRA Awards 1RC2MH089921-01, 1RC2MH090047-01, and 1RC2MH089929-01. © 2011. Available from: http://developinghumanbrain.org.

Page 32: an interspecies comparison of toxicity pathways mediating

Neuronal  Density  DistribuOon  

v

Page 33: an interspecies comparison of toxicity pathways mediating

Summary  (II)  

•  The Neurosphere assay needs specific algorithms for HCA: development of ‘Omnisphero’.

•  Composite fill and Neuron tracer significantly improve true neuronal detection rate as a ‘conventional’ HCA endpoint.

•  Sphere-specific endpoints like migration and neuronal positioning can be assessed by ‘Ominsphero’.

Page 34: an interspecies comparison of toxicity pathways mediating

Dr.  Marta  Barenys  Dr.  Julia  Tigges  Dr.  Susanne  Giersiefer  Dr.  JaneZe  Schuwald  Dr.  Henrik  Alm  Jenny  Baumann  Katharina  Dach  Mar>n  Schmuck  Maxi  Hofrichter  Stefan  Masjosthusmann  Chris>ne  Hellwig  Chris>ane  Hohensee  Laura  Nimtz  Denise  de  Boer  Ulrike  Hübenthal    

Thank  you  for  your  aaenOon!  

CooperaOon  partners:  Pamela  Lein,  UC  Davis,  USA  Heike  Heuer,  IUF,  Düsseldorf  Axel  Mosig,  University  of  Bochum  Kai  Stühler,  HHU  Düsseldorf    

Acknowledgements  

LRI Innovative Science Award 2006 German Alternative

Methods Award 2007

Leibniz - DAAD�

AOP  –  DNT:  

Page 35: an interspecies comparison of toxicity pathways mediating

DNT  –  TranslaOng  Time  

www.translatingtime.net Processes:  Brain  Growth  &  Neurogenesis,  whole  brain  

GW HUMAN

PC

DA

YS

1st trimester 3rd trimester 2nd trimester

0  

5  

10  

15  

20  

25  

30  

35  

4   6   8   10   12   14   16   18   20   22   24   26   28   30   32   34   36   38   40   42   44  

RAT  

MOUSE  

birth  

birth  

Clancy et al. Neuroinformatics 2007 Nagarajan et al. Neuroinformatics 2010