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BMC Ecology logoLink to BMC Ecology
. 2014 Aug 15;14:23. doi: 10.1186/1472-6785-14-23

Evidence for functional convergence in genes upregulated by herbivores ingesting plant secondary compounds

Jael R Malenke 1,, Michele M Skopec 2, M Denise Dearing 1
PMCID: PMC4153740  PMID: 25123454

Abstract

Background

Nearly 40 years ago, Freeland and Janzen predicted that liver biotransformation enzymes dictated diet selection by herbivores. Despite decades of research on model species and humans, little is known about the biotransformation mechanisms used by mammalian herbivores to metabolize plant secondary compounds (PSCs). We investigated the independent evolution of PSC biotransformation mechanisms by capitalizing on a dramatic diet change event—the dietary inclusion of creosote bush (Larrea tridentata)—that occurred in the recent evolutionary history of two species of woodrats (Neotoma lepida and N. bryanti).

Results

By comparing gene expression profiles of two populations of woodrats with evolutionary experience to creosote and one population naïve to creosote, we identified genes either induced by a diet containing creosote PSCs or constitutively higher in populations with evolutionary experience of creosote. Although only one detoxification gene (an aldo-keto reductase) was induced by both experienced populations, these populations converged upon functionally equivalent strategies to biotransform the PSCs of creosote bush by constitutively expressing aldehyde and alcohol dehydrogenases, Cytochromes P450s, methyltransferases, glutathione S-transferases and sulfotransferases. The response of the naïve woodrat population to creosote bush was indicative of extreme physiological stress.

Conclusions

The hepatic detoxification system of mammals is notoriously complex, with hundreds of known biotransformation enzymes. The comparison herein of woodrat taxa that differ in evolutionary and ecological experience with toxins in creosote bush reveals convergence in the overall strategies used by independent species after a historical shift in diet. In addition, remarkably few genes seemed to be important in this dietary shift. The research lays the requisite groundwork for future studies of specific biotransformation pathways used by woodrats to metabolize the toxins in creosote and the evolution of diet switching in woodrats. On a larger level, this work advances our understanding of the mechanisms used by mammalian herbivores to process toxic diets and illustrates the importance of the selective relationship of PSCs in shaping herbivore diversity.

Keywords: Herbivory, Diet switching, Mammalian herbivores, Neotoma, Biotransformation, Microarray

Background

For herbivorous animals, food ingestion can have deleterious consequences [1,2]. At every meal, herbivores confront potential toxins in the form of plant secondary compounds (PSCs). Some herbivores, e.g., the black swallowtail (Papilio polyxenes) and Stephen’s woodrat (Neotoma stephensi), have evolved the ability to specialize on plant species with high concentrations of PSCs, whereas other herbivores must consume undefended plants or small quantities of many species of plants with differing PSCs to keep toxin intake below threshold doses [3-6].

In general, diet selection and diet breadth of herbivores is thought to be governed by the capacity of biotransformation (detoxification) enzymes in the liver [7,8]. Major evolutionary dietary shifts seem to be enabled by an underlying change in biotransformation enzymes [9,10]. Surprisingly few alterations among myriad biotransformation enzymes are required for a change in the capacity to metabolize a new toxin. Insect resistance to pesticides and mammalian resistance to rodenticides can occur through the increased activity of a single biotransformation enzyme [9,11]. Currently, far more is known about the biotransformation mechanisms employed by insect herbivores in a diet shift than their mammalian counterparts [1,9,12].

The vast diversity of biotransformation enzymes presents a challenge in determining which enzymes enable the processing of a particular diet or toxin. For example, more than 300 hepatic biotransformation enzymes have been described for the laboratory rat, Rattus norvegicus (http://www.reactome.org, [13]). Enzyme activity assays exist for far fewer than the known number of biotransformation enzymes and are not always specific to a gene product [14]. To overcome these challenges, we took a genomic approach and used microarray technology customized for our study species, to identify, on a more global scale, biotransformation gene expression patterns involved in the processing of PSCs. Gene expression is an important phenotypic character, subject to selection from the environment [14-16]. Many recent studies have concluded that differences in gene expression among groups are the result of disparate selective forces [17-19].

We investigated the independent evolution of biotransformation mechanisms related to diet switching by capitalizing on a dramatic diet change event that occurred in the recent evolutionary history two species of woodrats (Neotoma lepida, N. bryanti). Both species underwent radical dietary changes due to floral shifts during the climate change event of the late Pleistocene and early Holocene (18,700-10,000 years ago). This event resulted in both of these woodrats independently switching from diets of juniper and/or cactus, to one containing creosote bush as it naturally invaded from Mexico and expanded to become the dominant shrub in the major deserts of the U.S. southwest [20,21]. Fossil records of middens of both species indicate that N. bryanti came into contact with creosote 7,000 years before N. lepida[22,23].

The change in diet to creosote from previous plant species represents a marked change in PSC composition. Juniper contains high concentrations of numerous terpenes as well as less abundant tannins [24,25]. The primary PSC in cactus (oxalate) is only degraded by gut microbes, not liver enzymes [26]. In contrast, creosote leaves produce a complex resin containing >300 compounds, primarily aromatic ones, which account for 10-25% of the leaf dry weight [27]. The principal component of resin is nordihydroguaiaretic acid (NDGA), a phenolic lignan with detrimental effects when administered to laboratory rats in doses regularly consumed by woodrats [28-30]. The distinct differences in the PSCs of juniper and cactus versus creosote suggest they are metabolized by different biotransformation pathways [14,31]. Comparative data on enzyme activities and gene expression of populations of N. lepida support this contention. Neotoma lepida that feed on juniper have different enzyme activity and gene expression profiles compared to those that feed on creosote even when they are fed the same diet [32-34]. Indeed, populations of N. lepida in the Mojave desert have adapted to a diet of creosote as evidenced by their ability to ingest greater quantities of creosote compared to those from the Great Basin desert that feed on juniper and have no prior exposure to creosote [35]. Less is known about the ancestral diet of N. bryanti and no data exist with respect to its ability to metabolize PSCs. However, a recent comparative study on gene expression in N. lepida and N. bryanti on a non-toxic diet revealed similarities in expression profiles in populations of both species that feed on creosote, relative to N. bryanti populations naïve to creosote [36]. These results are consistent with potential convergence in biotransformation strategies of N. lepida and N. bryanti with respect to metabolism of a creosote diet.

To advance our knowledge of the mechanisms involved in diet switching in mammals as well as biotransformation of PSCs in general, we addressed three questions. We asked which genes are induced (upregulated) by woodrats in response to the addition of creosote PSCs to the diet. Gene induction is a conventional pharmacological approach used to identify potentially important enzymes in biotransformation of foreign compounds. Second, we asked whether experience mattered with respect to the biotransformation of creosote. We contrasted the responses of woodrats that historically and currently consume creosote to a population that is ecologically and evolutionarily naïve to creosote compounds. Lastly, we asked whether there was convergence in the pathways used for biotransformation of creosote resin between N. bryanti and N. lepida that regularly fed on creosote bush by comparing the induced transcripts and also by contrasting their gene expression profiles.

Results

Feeding trial

All three populations maintained weight on both the control and creosote diet (Additional file 1: Table S1). However, there was a significant difference across populations with the experienced N. bryanti being heavier than the other two populations.

Microarray quality control

Four of the 24 arrays failed to pass all 9 of Agilent’s quality metrics. Three of these passed 8 of 9 metrics, and 1 passed 7 of 9. All were kept in the analysis. On average, less than 0.3% of the features across all arrays were flagged as non-uniform. The clustergram grouping individual woodrats by overall expression profile (all 6286 genes) grouped all the N. lepida in one monophyletic clade and each N. bryanti population in its own monophyletic clade, but did not group individuals by diet within species designations (Additional file 2: Figure S1).

Transcripts induced by creosote

Both species and all populations altered gene expression in response to the creosote diet compared to the control. The experienced N. bryanti had fewer induced (n = 7) and repressed transcripts (n = 7) than either the experienced N. lepida (induced n = 26, repressed n = 20) or the naïve N. bryanti (induced n = 18, repressed n = 9); however, the difference among the groups was not significant (Χ2 = 1.23 p = 0.54). There were no induced transcripts shared by all groups in this analysis. The experienced and naïve populations of N. bryanti shared two induced transcripts, one of which was for a biotransformation gene (aldo-keto reductase 7A3, Table 1). None of the treatment groups on creosote induced more than five different biotransformation genes (Table 1). The largest fold induction of a biotransformation transcript was observed in the naïve N. bryanti, which induced sulfotransferase 3A1 by 22×. All other biotransformation transcripts across all groups exhibited inductions of 7-fold or less.

Table 1.

Transcripts induced by creosote diet in three treatments: A. naïve N. bryanti , B. experienced N. bryanti and C. experienced N. lepida

  Gene ID Gene description Ratio p-value
A.
Induced in N. bryanti – naïve
 
 
 
NM_020565
Sulfotransferase family 3A, member 1
22.34
0.024497169
 
NM_021391
Protein phosphatase 1, regulatory (inhibitor) subunit 1A
12.42
0.005341544
 
NM_173295
UDP glucuronosyltransferase 2 family, polypeptide B17
3.3
0.01004607
 
NM_027153
Pirin, mRNA
3.18
0.049005275
 
NM_173295
UDP glucuronosyltransferase 2 family, polypeptide B17
2.95
0.005109673
 
NM_007631
Cyclin D1
2.75
0.047341015
 
NM_010145
Epoxide hydrolase 1, microsomal
2.51
0.004864803
 
NM_008761
*FXYD domain-containing ion transport regulator 5 transcript variant 2
2.51
0.005930014
 
NM_019144
Acid phosphatase 5, tartrate resistant
2.38
0.030204487
 
NM_016740
S100 calcium binding protein A11
2.37
0.002381142
 
NM_019693
HLA-B-associated transcript 1A
2.31
0.002135102
 
NM_013215
**Aldo-keto reductase family 7, member A3
2.2
0.048796617
 
NM_009673
Annexin A5
2.11
0.022303224
 
NM_010664
Keratin 18
2.08
0.034267738
 
NM_028070
AlkB, alkylation repair homolog 4 (E. coli)
2.07
0.026611663
 
NM_013899
Translocase of inner mitochondrial membrane 10 homolog (yeast)
2.04
0.001531745
 
NM_013058
Inhibitor of DNA binding 3
2.03
0.014931095
 
NM_001111030
Activin A receptor, type IC
2.02
0.015088922
B.
Induced in N. bryanti – experienced
 
 
 
NM_053346
Neuritin 1
3.99
0.016579939
 
NM_001164627
Rho GTPase activating protein 8 transcript variant 1, MutualBestHitTo
3.1
0.0205116
 
NM_013215
**Aldo-keto reductase family 7, member A3
2.93
0.005358317
 
NM_001109171
Leucine rich repeat containing 20
2.65
0.001865456
 
NM_008761
*FXYD domain-containing ion transport regulator 5 transcript variant 2
2.23
0.023632655
 
NM_027582
RIKEN cDNA 4921521 F21 gene
2.11
0.026277911
 
NM_001106470
Similar to KIAA1627 protein
2.05
0.027174423
C.
Induced in N. lepida – experienced
 
 
 
NM_027406
Aldehyde dehydrogenase 1 family, member L1
6.9
0.032217115
 
NM_029662
Major facilitator superfamily domain containing 2
5.01
0.009297156
 
NM_027406
Aldehyde dehydrogenase 1 family, member L1
4.5
0.023937762
 
NM_001014058
Ubiquitin specific peptidase 18
3.56
0.02525724
 
NM_001184980
Sulfotransferase family 2A DHEA-preferring member 5, SimilarTo
3.43
0.016254811
 
NM_031004
Smooth muscle alpha-actin
3.37
0.025794253
 
NM_001126273
AlkB, alkylation repair homolog 2 (E. coli)
3.26
0.047075352
 
NM_177200
SV2 related protein homolog (rat)-like
3.25
0.007639427
 
NM_010145
Epoxide hydrolase 1, microsomal
2.99
0.013289403
 
NM_178686
Centrosomal protein 120
2.92
0.012963163
 
NM_010358
Glutathione S-transferase, mu 1
2.8
0.022522125
 
NM_001168541
Tsukushin transcript variant 1, MutualBestHitTo
2.75
0.007592024
 
NM_022331
Ubiquitin-like domain member 1
2.64
0.004966041
 
NM_001184980
Sulfotransferase family 2A DHEA-preferring member 5, SimilarTo
2.45
0.036858859
 
NM_031768
Integrin, alpha E, epithelial-associated
2.4
0.035330416
 
NM_198780
Phosphoenolpyruvate carboxykinase 1 (soluble)
2.4
0.047233237
 
NM_011393
Solute carrier family 1, member 2, transcript variant 3
2.37
0.000661494
 
NM_145123
Cartilage acidic protein 1
2.27
0.028029577
 
NM_133626
Ribosome binding protein 1
2.27
0.042370631
 
NM_029494
RAB30, member RAS oncogene family
2.19
0.030712931
 
NM_153392
Tetratricopeptide repeat domain 39A, transcript variant 2
2.15
0.044515732
 
NM_138953
Elongation factor RNA polymerase II 2
2.13
0.017500695
 
NM_022602
Pim-3 oncogene
2.06
0.018759684
 
NM_053433
Flavin containing monooxygenase 3
2.03
0.01753571
 
NM_028116
Pygopus 1
2.02
0.002651983
  NM_021390 Zinc finger protein Sall1 2.0 0.006073039

Bolded entries have known detoxification function. Asterisks indicate transcripts that are induced in both categories A and B. There are no shared induced transcripts between B and C.

Differential expression between naïve and experienced woodrats

There were significant differences in expression related to experience with creosote between N. bryanti populations. Although the total number of transcripts with greater expression in both the experienced and naïve was similar (199 in experienced vs. 183 naïve, [Table 2A with list of genes in Additional file 3: Table S2]), the experienced population expressed absolutely twice as many transcripts for biotransformation enzymes (Table 2A, Χ2 = 14.72, df = 1, p < 0.001). Proportionally, 37% of all transcripts expressed to a greater degree by experienced N. bryanti were biotransformation related compared to only 18% of those in the naïve N. bryanti. Many of the differentially regulated biotransformation transcripts coded for the same Genbank accession. The effective gene numbers, calculated from Shannon’s H, reflected the same pattern as the total biotransformation transcript counts. For naïve N. bryanti the effective gene number was 19.7 compared to an effective gene number for experienced N. bryanti of 34.8.

Table 2.

Number of transcripts with significantly different expression in a comparison of (A) naïve and experienced N. bryanti on the creosote diet and (B) experienced N. bryanti and N. lepida on the creosote diet

A.   Transcripts  
Treatment population
All
Detox
Chi-square
 
Higher expression, N. bryanti, naïve
183
35
Χ2 = 11.92, df = 1, p < 0.001
 
Higher expression, N. bryanti, experienced
199
76
B.
 
 
 
Treatment species
All
Detox
Chi-square
 
Higher expression, N. bryanti, experienced
134
69
Χ2 = 14.72, df = 1, p = 0.0001
  Higher expression, N. lepida, experienced 109 23

Chi square analyses compare the number of detoxification genes with higher expression to the overall number of genes with higher expression across the two experimental groups.

The degree to which upregulated genes were expressed was greater, overall, in the experienced N. bryanti (Table 3, Additional file 3: Table S2). The biotransformation transcript with the greatest expression in naïve N. bryanti and the only one with more than 10-fold higher expression in naïve compared to experienced animals, was a cytochrome P450 (2C65). In contrast, there were three biotransformation transcripts in the experienced N. bryanti that exceeded 10-fold higher expression compared to naïve N. bryanti. These transcripts are related to the functionalization of aldehydes (aldo-keto reductase 1C12) and glucuronic acid and glutathione conjugation pathways (UDP glucuronosyltransferase 2B34, glutathione S-transferase, mu 7).

Table 3.

Transcripts associated with detoxification function with significantly greater expression in (A) naive N. bryanti relative to experienced N. bryanti and (B.) experienced N. bryanti relative to naïve N. bryanti

  Gene ID Gene description Ratio p-value
A.
Greater expression in naïve N. bryanti
 
 
Phase I - catalyze oxidation, reduction and hydrolysis reactions
 
 
 
Alcohol dehydrogenases - oxidize alcohols
 
NM_009626
C57BL/6 J alcohol dehydrogenase class 4
2.11
0.019591
 
Carboxylesterases - hydrolyze carboxylic acid esters
 
NM_145603
Carboxylesterase 2
2.52
0.001284
 
NM_145603
Carboxylesterase 2
2.52
0.001213
 
NM_021456
Carboxylesterase 1
2.45
0.036796
 
NM_021456
Carboxylesterase 1
2.36
0.040035
 
NM_172759
Carboxylesterase 5,
2.12
0.001463
 
Cytochromes P450 - oxidize wide range of organic substrates
 
NM_028191
Cytochrome P450, family 2, subfamily c, polypeptide 65
15.62
0.006602
 
NM_007825
Cytochrome P450, family 7, subfamily b, polypeptide 1
4.48
0.000458
 
XM_219933
PREDICTED: P450 family 2 subfamily c polypeptide 79, SimilarTo
4.43
0.001591
 
NM_028191
Cytochrome P450, family 2, subfamily c, polypeptide 65
3.79
0.009243
 
NM_007825
Cytochrome P450, family 7, subfamily b, polypeptide 1,
3.24
0.001260
 
NM_019138
Cytochrome P450, family 7, subfamily b, polypeptide 1
2.46
0.002067
 
NM_019138
Cytochrome P450, family 7, subfamily b, polypeptide 1
2.2
0.002338
 
NM_010009
25-hydroxyvitamin D3 1alpha-hydroxylase
2.12
0.021096
 
Flavin containing monooxygenases - oxidize amines
 
NM_018881
Flavin containing monooxygenase 2, mRNA
2.78
0.018212
 
NM_018881
Flavin containing monooxygenase 2, mRNA
2.66
0.026835
 
 
Phase II - catalyze transfer of conjugates to metabolites
 
 
 
Acetyltransferases - transfer acetyl conjugate
 
NM_001161712
Glycine C-acetyltransferase transcript variant 2 SimilarTo
3.45
0.015595
 
UDP glucuronosyltransferases - transfer glucuronic acid conjugate
 
NM_172881
UDP glucuronosyltransferase 2 family, polypeptide B35
3.93
0.048799
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
2.86
0.000686
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
2.6
0.000899
 
NM_001029867
UDP glucuronosyltransferase 2 family, polypeptide B36
2.02
0.000218
 
Glutathione S-transferases - transfer glutathione conjugate
 
NM_012577
Glutathione S-transferase pi
2.67
0.003827
 
Methyltransferases - transfer methyl group conjugate
 
NM_016785
Thiopurine methyltransferase
5.2
0.000140
 
NM_016785
Thiopurine methyltransferase
5.04
0.000190
 
NM_016785
Thiopurine methyltransferase
4.72
0.000223
 
NM_016785
Thiopurine methyltransferase
4.3
0.000073
 
NM_022884
Betaine-homocysteine methyltransferase 2
3.48
0.001257
 
NM_022884
Betaine-homocysteine methyltransferase 2
2.15
0.005312
 
NM_026440
RNA (guanine-7-) methyltransferase
2.12
0.004311
 
NM_022884
Betaine-homocysteine methyltransferase 2
2.11
0.005705
 
NM_177846
MKIAA0547 protein
2.04
0.000481
 
Sulfotransferases - tranfer sulfo group conjugate
 
NM_001184980
Sulfotransferase family 2A DHEA-preferring member 5, SimilarTo
4.75
0.006821
 
NM_001101586
Sulfotransferase family 2A DHEA-preferring member 5, SimilarTo
4.73
0.020208
 
NM_001101586
Sulfotransferase family 2A DHEA-preferring member 5, SimilarTo
4.69
0.025323
 
NM_001101534
CDNA clone IMAGE:9053718
4.11
0.031920
B.
Greater expression in experienced N. bryanti
 
 
Phase I - catalyze oxidation, reduction and hydrolysis reactions
 
 
 
Aldo-keto reductases - oxidize and reduce aldehydes and ketones
 
NM_013777
Aldo-keto reductase family 1, member C12
22.98
0.000139
 
NM_030611
Aldo-keto reductase family 1, member C6
7.65
0.000074
 
Aldehyde dehydrogenases - oxidize aldehydes
 
NM_153543
Aldehyde dehydrogenase 1 family, member L2
3.61
0.000215
 
NM_031057
Aldehyde dehydrogenase 6 family, member A1
2.19
0.046613
 
Carboxylesterases - hydrolyze carboxylic acid esters
 
NM_145603
Carboxylesterase 2
6.91
0.000264
 
NM_001190346
Carboxylesterase 2 transcript variant 2, SimilarTo
6.55
0.000143
 
NM_145603
Carboxylesterase 2
6.21
0.000575
 
NM_001044258
Similar to Carboxylesterase 2
6.04
0.000027
 
NM_001044258
Similar to Carboxylesterase 2
5.68
0.000028
 
NM_001190346
Carboxylesterase 2, transcript variant 2, SimilarTo
3.63
0.000532
 
NM_172759
Carboxylesterase 5
2.9
0.001251
 
Cytochromes P450 - oxidize wide range of organic substrates
 
NM_023025
Cytochrome P450, family 2, subfamily J, polypeptide 4
6.7
0.002710
 
NM_012730
Cytochrome P450, family 2, subfamily d, polypeptide 2
3.38
0.035947
 
NM_012730
Cytochrome P450, family 2, subfamily d, polypeptide 2
3.34
0.019677
 
NM_012730
Cytochrome P450, family 2, subfamily d, polypeptide 2
3.25
0.047435
 
NM_153312
Cytochrome P450, family 3, subfamily a, polypeptide 23/polypeptide 1
3.1
0.006788
 
NM_153312
Cytochrome P450, family 3, subfamily a, polypeptide 23/polypeptide 1
2.92
0.000334
 
NM_022434
Cytochrome P450, family 4, subfamily f, polypeptide 14
2.34
0.002319
 
Flavin containing monooxygenases - oxidize amines
 
NM_001161765
Flavin containing monooxygenase 5 transcript variant 1, SimilarTo
2.46
0.005855
 
NM_001161765
Flavin containing monooxygenase 5 transcript variant 1, SimilarTo
2.4
0.006221
 
Miscellaneous Phase I
 
NM_013626
Peptidylglycine alpha-amidating monooxygenase
2.23
0.005322
 
NM_001004086
Paraoxonase 3
2.18
0.000331
 
 
Phase II - catalyze transfer of conjugates to metabolites
 
 
 
Acetyltransferases - transfer acetyl conjugate
 
NM_053853
N-acetyltransferase 1
7.05
0.000017
 
NM_001108278
Spermidine/spermine N1-acetyltransferase family member 2
6.26
0.000021
 
NM_053853
N-acetyltransferase 1
5.39
0.000007
 
NM_053853
N-acetyltransferase 1
4.99
0.000010
 
NM_001006995
Acetyl-Coenzyme A acetyltransferase 2
3.73
0.004937
 
NM_001009657
Histone acetyltransferase 1
2.24
0.000395
 
NM_001009657
Histone acetyltransferase 1
2.04
0.000004
 
UDP glucuronosyltransferases - transfer glucuronic acid conjugate
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
11.7
0.000347
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
7.22
0.013582
 
NM_201642
UDP glucuronosyltransferase 1 family, polypeptide A6B
5.21
0.000008
 
NM_152811
UDP glucuronosyltransferase 2 family, polypeptide B1
3.37
0.043313
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
2.24
0.004634
 
NM_001191676
UDP glucuronosyltransferase 2 family polypeptide B34, SimilarTo
2.18
0.005383
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
2.06
0.007980
 
Glutathione S-transferases - transfer glutathione conjugate
 
NM_026672
Glutathione S-transferase, mu 7
10.47
0.038865
 
NM_026672
Glutathione S-transferase, mu 7
9.14
0.034704
 
NM_133994
Glutathione S-transferase, theta 3
8.12
0.003689
 
NM_133994
Glutathione S-transferase, theta 3
7.66
0.002784
 
NM_008183
Glutathione S-transferase, mu 2
4.77
0.000073
 
NM_008183
Glutathione S-transferase, mu 2
2.68
0.015619
 
NM_001024361
Similar to Glutathione S-transferase A1
2.54
0.040554
 
XM_001473911
PREDICTED: Glutathione S-transferase Mu 2, SimilarTo
2.41
0.000974
 
NM_001024304
Glutathione S-transferase mu 4
2.11
0.026064
 
NM_008183
Glutathione S-transferase, mu 2
2.09
0.001695
 
NM_001009920
Glutathione S-transferase Yc2 subunit
2.04
0.031287
 
Methyltransferases - transfer methyl group conjugate
 
NM_001008299
RNA (guanine-7-) methyltransferase
6.35
0.000009
 
NM_022884
Betaine-homocysteine methyltransferase 2
3.45
0.001721
 
NM_001106470
Similar to KIAA1627 protein
3.35
0.002862
 
NM_010321
Glycine N-methyltransferase
3.26
0.000333
 
NM_173765
Aminoadipate-semialdehyde dehydrogenase
3.02
0.000019
 
NM_010321
Glycine N-methyltransferase
2.84
0.000468
  NM_027334 Methyltransferase like 7A 2.73 0.002067

All animals were fed a creosote diet. Within populations, results are organized by major detoxification enzyme class. Duplicates indicate the response of multiple probes for a given gene.

Significant Gene Ontology (GO) terms (within biological process) were different in the naïve versus experienced N. bryanti. Before comparison, terms across ontology tiers were filtered to include only those with significant, positive z-scores (>2) and ordered by the number of genes in each ontology term. GO terms are reported only if they include 10 or more genes from the array. Naïve N. bryanti had more than twice the number of GO terms that passed these criteria. The top terms related to responses to stimuli; many of the other terms related to stress, damage and cell death (Table 4A). The experienced N. bryanti had fewer significant terms; the function of these related largely to metabolic processes (Table 4B).

Table 4.

Gene ontology (GO) terms overrepresented in (A) naïve N. bryanti and (B) experienced N. bryanti on creosote diets

Ontology List Gene set z-score
A. naïve N. bryanti
 
 
 
response to stimulus
61
1241
3.66
response to chemical stimulus
30
533
3.13
system development
28
587
2.06
response to stress
27
525
2.44
immune system process
22
265
4.62
apoptosis
20
350
2.56
cell death
20
367
2.34
death
20
370
2.3
programmed cell death
20
353
2.52
regulation of multicellular organismal process
20
328
2.88
regulation of apoptosis
17
287
2.51
regulation of cell death
17
297
2.35
regulation of programmed cell death
17
289
2.47
cellular response to chemical stimulus
15
222
2.89
immune response
15
140
4.92
regulation of developmental process
15
244
2.5
response to external stimulus
13
189
2.75
regulation of multicellular organismal development
12
206
2.02
defense response
11
147
2.83
positive regulation of developmental process
11
113
3.82
response to wounding
11
137
3.09
hemopoiesis
10
103
3.63
hemopoietic or lymphoid organ development
10
106
3.52
immune system development
10
115
3.23
negative regulation of apoptosis
10
145
2.41
negative regulation of cell death
10
153
2.23
negative regulation of programmed cell death
10
145
2.41
B. experienced N. bryanti
 
 
 
metabolic process
96
2711
2.39
small molecule metabolic process
35
782
2.51
response to chemical stimulus
25
533
2.3
cellular ketone metabolic process
23
332
4.23
carboxylic acid metabolic process
22
321
4.07
organic acid metabolic process
22
328
3.96
oxoacid metabolic process
22
321
4.07
amine metabolic process
13
203
2.81
cellular amine metabolic process
12
181
2.82
cellular amino acid metabolic process
11
152
3.02
monocarboxylic acid metabolic process 10 157 2.43

“List” indicates the number of genes highly expressed within the term; “Gene set” indicates the total number of genes in that ontology included on the array.

Differential expression between experienced woodrats of two species

The experienced N. bryanti had increased expression of more transcripts than N. lepida (134 vs 109) as well as a greater degree to which those genes were expressed (Additional file 4: Table S3). This result was also true with respect to the biotransformation transcripts alone; N. bryanti had greater expression of 3× more transcripts compared to N. lepida on creosote and, in general, these genes were expressed to a much higher degree (Table 2B and Table 5). The effective gene numbers also reflect this pattern. The effective gene number with greater expression in N. bryanti was 20.7, whereas the effective gene number for N. lepida was 14.4.

Table 5.

Transcripts associated with detoxification function with significantly greater expression in (A.) experienced N. bryanti relative to N. lepida and (B.) experienced N. lepida relative to N. bryanti

  Gene ID Gene Description Ratio p-value
A.
Greater expression in experienced N. bryanti
 
 
 
 
Phase I - catalyze oxidation, reduction & hydrolysis reactions
 
 
 
Aldehyde dehydrogenases - oxidize aldehydes
 
 
 
NM_178713
Aldehyde dehydrogenase 8 family, member A1
2.22
0.010400
 
Alcohol dehydrogenases - oxidize alcohols
 
 
 
NM_017270
Alcohol dehydrogenase 4 (class II), pi polypeptide
3.03
0.005872
 
NM_017270
Alcohol dehydrogenase 4 (class II), pi polypeptide
2.82
0.005802
 
NM_017270
Alcohol dehydrogenase 4 (class II), pi polypeptide
2.32
0.000857
 
NM_017270
Alcohol dehydrogenase 4 (class II), pi polypeptide
2.26
0.002058
 
Carboxylesterases - hydrolyze carboxylic acid esters
 
 
 
NM_001190346
Carboxylesterase 2 transcript variant 2, SimilarTo
2.61
0.003223
 
XR_033674
PREDICTED: similar to Carboxylesterase 2
2.28
0.000942
 
NM_001190346
Carboxylesterase 2 transcript variant 2. SimilarTo
2.24
0.002730
 
NM_001190346
Carboxylesterase 2 transcript variant 2. SimilarTo
2.04
0.021685
 
Cytochromes P450 - oxidize wide range of organic substrates
 
 
 
NM_008898
P450 (cytochrome) oxidoreductase
2.36
0.013012
 
NM_147206
Cytochrome P450, family 3, subfamily a, polypeptide 9
2.18
0.021999
 
NM_147206
Cytochrome P450, family 3, subfamily a, polypeptide 9
2.09
0.023839
 
NM_153312
Cytochrome P450, family 3, subfamily a, polypeptide 23/polypeptide 1
2.08
0.014854
 
Flavin containing monooxygenases - oxidize amines
 
 
 
NM_008030
Flavin containing monooxygenase 3
2.52
0.004188
 
Superoxide dismutases - dismutase superoxide to oxygen and water
 
 
 
NM_017050
Superoxide dismutase 1
2.17
0.007301
 
 
Phase II - catalyze transfer of conjugates to metabolites
 
 
 
UDP glucuronosyltransferases - transfer glucuronic acid conjugate
 
 
 
NM_152811
UDP glucuronosyltransferase 2 family, polypeptide B1
26.84
0.000202
 
NM_152811
UDP glucuronosyltransferase 2 family, polypeptide B1
26.2
0.000230
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
13.03
0.000721
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
10.82
0.001924
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
8.52
0.000934
 
NM_152811
UDP glucuronosyltransferase 2 family, polypeptide B1
7.33
0.000471
 
NM_152811
UDP glucuronosyltransferase 2 family, polypeptide B1
7.05
0.001293
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
4.58
0.003637
 
NM_173295
UDP glucuronosyltransferase 2 family, polypeptide B17
4.23
0.004670
 
NM_173295
UDP glucuronosyltransferase 2 family, polypeptide B17
4.16
0.004114
 
NM_173295
UDP glucuronosyltransferase 2 family, polypeptide B17
3.82
0.006675
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
3.79
0.003846
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
3.2
0.000542
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
3.13
0.000852
 
NM_001191676
UDP glucuronosyltransferase 2 polypeptide B34, SimilarTo
2.8
0.003254
 
NM_153598
UDP glucuronosyltransferase 2 family, polypeptide B34
2.64
0.001950
 
NM_001191676
UDP glucuronosyltransferase 2 family polypeptide B34
2.52
0.010507
 
NM_201642
UDP glucuronosyltransferase 1 family, polypeptide A6B
2.34
0.009381
 
NM_009467
UDP glucuronosyltransferase 2 family, polypeptide B5
2.23
0.003903
 
NM_201642
UDP glucuronosyltransferase 1 family, polypeptide A6B
2.23
0.005852
 
Glutathione S-transferases - transfer glutathione conjugate
 
 
 
NM_012796
Glutathione S-transferase, theta 2
5.9
0.002555
 
NM_012796
Glutathione S-transferase, theta 2
4.93
0.003108
 
NM_012796
Glutathione S-transferase, theta 2
4.79
0.003690
 
NM_001024361
Similar to Glutathione S-transferase A1
3.98
0.005397
 
NM_001024361
Similar to Glutathione S-transferase A1
3.58
0.008732
 
NM_001024361
Similar to Glutathione S-transferase A1
3.52
0.005938
 
NM_001024361
Similar to Glutathione S-transferase A1
3.25
0.014456
 
NM_012796
Glutathione S-transferase, theta 2
2.89
0.032248
 
NM_001024361
Similar to Glutathione S-transferase A1
2.66
0.008524
 
NM_001024361
Similar to Glutathione S-transferase A1
2.39
0.010509
 
NM_008183
Glutathione S-transferase, mu 2
2.34
0.047800
 
NM_001009920
Glutathione S-transferase Yc2 subunit
2.32
0.018875
 
NM_001009920
Glutathione S-transferase Yc2 subunit
2.1
0.025697
 
NM_001077353
Glutathione S-transferase, alpha 3, transcript variant 2
2.08
0.048535
 
Methyltransferases - transfer methyl group conjugate
 
 
 
NM_009349
Indolethylamine N-methyltransferase
10.85
0.000877
 
NM_009349
Indolethylamine N-methyltransferase
8.38
0.002392
 
NM_009349
Indolethylamine N-methyltransferase
6.52
0.009050
 
NM_009349
Indolethylamine N-methyltransferase
6.47
0.007757
 
NM_080462
Histamine N-methyltransferase
2.13
0.004838
 
XM_223974
Methyltransferase 11 domain containing 1
2.04
0.005653
 
NM_172687
Coenzyme Q3 homolog, methyltransferase (yeast)
2.03
0.008959
 
Sulfotransferases - tranfer sulfo group conjugate
 
 
 
NM_020565
Sulfotransferase family 3A, member 1
4.17
0.006575
 
NM_020565
Sulfotransferase family 3A, member 1
3.81
0.001338
 
NM_020565
Sulfotransferase family 3A, member 1
3.52
0.007965
 
NM_018805
Heparan sulfate (glucosamine) 3-O-sulfotransferase 3B1
3.22
0.001553
 
NM_020565
Sulfotransferase family 3A, member 1
3.2
0.000616
 
NM_020565
Sulfotransferase family 3A, member 1
2.83
0.004497
 
NM_031834
Sulfotransferase family, cytosolic, 1A, phenol-preferring, member 1
2.79
0.001314
 
NM_020565
Sulfotransferase family 3A, member 1
2.77
0.006085
 
NM_018805
Heparan sulfate (glucosamine) 3-O-sulfotransferase 3B1
2.75
0.000909
 
NM_020565
Sulfotransferase family 3A, member 1
2.53
0.000740
 
NM_031834
Sulfotransferase family, cytosolic, 1A, phenol-preferring, member 1
2.26
0.003965
 
NM_031834
Sulfotransferase family, cytosolic, 1A, phenol-preferring, member 1
2.05
0.004712
 
NM_020565
Sulfotransferase family 3A, member 1
2.04
0.024154
B.
Greater expression in experienced N. lepida
 
 
 
 
Phase I - catalyze oxidation, reduction & hydrolysis reactions
 
 
 
Aldehyde dehydrogenases - oxidize aldehydes
 
 
 
NM_027406
Aldehyde dehydrogenase 1 family, member L1
9.62
0.030847
 
NM_027406
Aldehyde dehydrogenase 1 family, member L1
4.11
0.045209
 
Alcohol dehydrogenases - oxidize alcohols
 
 
 
NM_007410
Alcohol dehydrogenase 5 (class III), chi polypeptide
2.14
0.025440
 
Cytochromes P450 - oxidize wide range of organic substrates
 
 
 
NM_028191
Cytochrome P450, family 2, subfamily c, polypeptide 65
8.87
0.017817
 
NM_007820
Cytochrome P450, family 3, subfamily a, polypeptide 16
3.69
0.006413
 
NM_019138
Cytochrome P450, family 7, subfamily b, polypeptide 1
2.68
0.015580
 
NM_007815
Cytochrome P450, family 2, subfamily c, polypeptide 29
2.53
0.028674
 
NM_023025
Cytochrome P450, family 2, subfamily J, polypeptide 4
2.45
0.004241
 
NM_010009
25-hydroxyvitamin D3 1alpha-hydroxylase
2.37
0.030007
 
 
Phase II - catalyze transfer of conjugates to metabolites
 
 
 
Glutathione S-transferases - transfer glutathione conjugate
 
 
 
NM_010358
Glutathione S-transferase, mu 1*
2.99
0.021783
 
NM_010358
Glutathione S-transferase, mu 1*
2.94
0.009552
 
NM_017013
Glutathione S-transferase A2
2.38
0.007870
 
NM_017013
Glutathione S-transferase A2
2.34
0.010162
 
NM_017013
Glutathione S-transferase A2
2.29
0.010172
 
Methyltransferases - transfer methyl group conjugate
 
 
 
NM_030241
SET domain containing (lysine methyltransferase) 8
2.19
0.001281
 
NM_025907
Methyltransferase like 6
2.05
0.019380
 
NM_016668
Betaine-homocysteine methyltransferase
2.04
0.013408
 
Sulfotransferases - tranfer sulfo group conjugate
 
 
 
NM_001101534
CDNA clone IMAGE:9053718
2.21
0.007280
 
NM_027928
Carbohydrate (chondroitin 4) sulfotransferase 13, MutualBestHitTo
2.07
0.006258
 
NM_027928
Carbohydrate (chondroitin 4) sulfotransferase 13, MutualBestHitTo
2.04
0.006510
  NM_027928 Carbohydrate (chondroitin 4) sulfotransferase 13, MutualBestHitTo 2.01 0.009812

Within species, results are organized by major detoxification enzyme classes. Duplicates indicate the response of multiple probes for a given gene.

In experienced N. bryanti, transcripts with the greatest expression were related to conjugation of metabolites with glucuronic acid (different glucuronosyltransferases) followed by those related to conjugation with glutathione (glutathione S-transferases; Table 5). In N. lepida, the transcripts with the highest expression were those related to functionalization of aldehydes by aldehyde dehydrogenase (1 L1) and oxidation by Cytochrome P450 (2C65). Compared to N. bryanti, N. lepida also had greater expression of some of the same transcripts that were significantly induced by creosote feeding, i.e., aldehyde dehydrogenase (1 L1) glutathione S-transferase mu-1 (Tables 1 and 5).

Significant GO terms overrepresented by experienced N. bryanti fed creosote were characterized by metabolic and catabolic processes as well as responses to stimuli (Table 6A). GO terms overrepresented by experienced N. lepida are characterized by responses to stimuli and signaling functions (Table 6B).

Table 6.

Gene ontology (GO) terms overrepresented in (A) N. bryanti and (B) N. lepida on a creosote diet

Ontology List Gene set z-score
A. experienced N. bryanti
 
 
 
metabolic process
65
2711
2.58
response to stimulus
36
1241
2.73
small molecule metabolic process
30
782
4.09
cellular response to stimulus
26
882
2.28
catabolic process
24
626
3.57
cellular catabolic process
21
550
3.28
response to chemical stimulus
18
533
2.44
oxidation-reduction process
17
375
3.68
cellular ketone metabolic process
15
332
3.42
carboxylic acid metabolic process
14
321
3.15
organic acid metabolic process
14
328
3.06
oxoacid metabolic process
14
321
3.15
response to organic substance
14
348
2.82
small molecule catabolic process
13
282
3.25
lipid metabolic process
12
316
2.38
cellular response to chemical stimulus
10
222
2.74
response to endogenous stimulus
10
186
3.37
B. experienced N. lepida
 
 
 
response to stimulus
35
1241
2.13
Signaling
25
764
2.52
signal transduction
24
689
2.79
regulation of response to stimulus
16
430
2.49
intracellular signal transduction
15
347
3.03
oxidation-reduction process
15
375
2.7
regulation of signal transduction
15
327
3.28
regulation of signaling
15
363
2.84
lipid metabolic process 13 316 2.61

“List” indicates the number of genes highly expressed within the term; “Gene set” indicates the total number of genes in that ontology included on the array.

Discussion

Despite the vast knowledge of drug-metabolizing enzymes in humans and model species, the biotransformation mechanisms used by mammalian herbivores to metabolize PSCs are largely unknown. Until recently, many studies were limited to analysis of one or a few biotransformation enzymes [32,37-40]. This study took advantage of microarray technology customized for a unique study system to address this deficit in our understanding. We investigated, on a transcriptomic scale, the genes induced by a particular suite of PSCs (creosote resin) and evaluated whether a common set of genes were expressed by herbivores with varying levels of evolutionary experience with these PSCs. We explored whether experienced herbivores have independently converged on regulation of a similar set of biotransformation genes. We found that biotransformation enzyme expression does indeed vary with ecological and evolutionary experience with creosote and that independent woodrat lineages employ, in part, similar strategies for successfully dealing with these shared PSCs. In addition, the results narrow the field from hundreds of possible biotransformation genes to less than ten candidates. The work provides a testable framework for the changes in expression of biotransformation enzymes that may have occurred as woodrats shifted from one toxic diet to another.

Induced biotransformation genes

We identified a narrow set of candidate genes relevant to the biotransformation of creosote. Surprisingly few biotransformation transcripts were induced by any of the groups fed creosote resin compared to the control diet. Of the hundreds of biotransformation enzymes, only four unique biotransformation transcripts were induced in the naïve N. bryanti, six in the experienced N. lepida, and in the experienced N. bryanti, only a single biotransformation enzyme, an aldo-keto reductase (AKR7A3) was induced (Table 1). All of these transcripts encode for enzymes that act on substrates similar to the compounds present in creosote, particularly aromatic compounds [27,31]. These enzymes could function in tandem as a pathway to produce the final metabolite excreted in urine and/or feces [41]. For example, epoxide hydrolase acts on aromatic compounds such as naphthalene epoxide whose parent compound, napthalene, is present in creosote [41]. AKR enzymes, in turn, act on the metabolites produced by epoxide hydrolase, whereas glutathione S-transferases and UDP glucuronosyltransferases add conjugates to the metabolites of AKR [42]. Thus, although few transcripts were induced in woodrats fed creosote, those induced transcripts produce enzymes that act on substrates similar to those in resin. Furthermore, the candidate genes identified could function in concert with one another in the biotransformation of PSCs in creosote.

Few of the transcripts induced by the creosote diet were shared across woodrat groups. The conspecific populations shared induction of AKR7A3. The superfamily of AKR enzymes act on a broad variety of substrates, particularly aldehydes and ketones, and the 7A3 isoform metabolizes aflatoxin B1 [42]. Epoxide hydrolase was induced by the naïve N. bryanti and experienced N. lepida, and also the experienced N. bryanti but in this case, at less than the 2-fold cut-off. This enzyme adds water to epoxides that could otherwise cause toxicity or mutation [31]. Epoxides are often formed during the biotransformation of aromatic hydrocarbons [31], which are common in creosote resin [27]. The shared induction across all three groups of woodrats suggests epoxide hydrolase could be critical to the biotransformation of resin. Lastly, the naïve N. bryanti and experienced N. lepida induced different sulfotransferases. This superfamily has high affinity to myriad substrates and metabolizes compounds (e.g., polyaromatic hydrocarbons) present in creosote resin [31]. Sulfotransferases biotransform xenobiotics by the addition of a sulfur co-factor, generated from dietary cysteine. Because the availability of cysteine is often limited, sulfation capacity is often much lower than other conjugation pathways. It is possible that the woodrat diet contains ample cysteine or its precursors, serine and methionine. Consistent with this idea, both experienced populations upregulated methyltransferases involved in serine and methionine metabolism (Tables 3 and 5). Alternatively, sulfation capacity may be greater in woodrats compared to other mammals. However, previous work suggests the capacity for sulfation is exceeded in both naïve and experienced N. lepida at low levels of creosote ingestion [43]. The role that sulfation plays in the biotransformation of creosote resin deserves further attention.

Alterations in biotransformation mechanisms as a result of diet shifts

The change by woodrats from an ancestral diet of juniper and/or cactus to that of creosote likely required a different set of biotransformation enzymes to process the disparate suites of PSCs in these plants. The naïve and experienced N. bryanti had increased expression of about the same number of genes on creosote compared to the control diet. However, within that pool of genes, the naïve N. bryanti expressed fewer transcripts with biotransformation functions than the experienced animals. A similar pattern has been observed elsewhere; woodrats feeding on a novel diet (i.e., animals naïve to the diet) expressed relatively few biotransformation transcripts and more transcripts related to cellular function compared to feeding on their native diet [33]. The animals on the novel diet were thought to be unable to marshal the appropriate biotransformation response, and the upregulation of genes with diverse cellular functions may have been to prevent or respond to the physiological consequences of the PSCs. Indeed, the functional analyses of the gene ontologies for differentially expressed genes in N. bryanti are consistent with this hypothesis (Table 4). The transcriptomes of naïve woodrats were enriched in GO classes related to considerable physiological stresses (e.g., death, response to wounding). In contrast, those enriched in experienced N. bryanti were related to the processing of toxins.

Functional convergence

There is evidence for functional convergence between the two species with respect to the transcripts induced on a creosote diet. As discussed above, the transcript for epoxide hydrolase was the only biotransformation transcript significantly induced by both species; however, it was expressed at levels below the 2-fold cut-off used in the initial analysis. The top biotransformation transcript induced by N. lepida (aldehyde dehydrogenase) and the only biotransformation transcript induced by N. bryanti (aldo-keto reductase) both encode for enzymes that metabolize similar substrates, particularly aldehydes. Creosote resin contains at least 300 compounds, including aldehydes and compounds that may have aldehyde functional groups after biotransformation by other enzymes [27,44]. Aldehydes are reactive compounds that cause considerable cellular damage. Inadequacies in the biotransformation of aldehydes are connected to a number of human diseases [45,46]. Given the potential for damage, aldehydes in creosote are likely a significant selective force resulting in the convergence on the induction of transcripts related to aldehyde metabolism by both species.

Further demonstration that the two experienced woodrats exhibit a parallel response to the ingestion of creosote resin is witnessed in their overall gene expression patterns. Many of the biotransformation transcripts that were more highly expressed in the experienced N. bryanti have analogous functions with those that were more highly expressed in N. lepida (Table 5). For example, both species have higher expression of different isoforms of aldehyde dehydrogenases (ALDH8A1 versus ALDH1L1). A similar pattern is present for alcohol dehydrogenases, Cytochromes P450, methyltransferases, glutathione S-transferases, and sulfotransferases. One notable exception to this pattern is that N. lepida did not have a corollary in the UDP-glucuronosyltransferases (UGTs), a superfamily of biotransformation enzymes responsible for glucuronidation. Neotoma bryanti had higher expression of at least 6 different UGTs, one of which was expressed 26 fold higher. The UGTs are considered some of the most versatile of the conjugation enzymes due to their wide range of substrates [31]. Previous studies reported that N. lepida fed creosote increased glucuronidation thereby demonstrating it is indeed an important pathway in N. lepida[32,43]. It is possible that both species use the same UGTs for creosote biotransformation but that N. bryanti utilizes this pathway to a greater extent resulting in the higher gene expression values observed in this study.

The last line of evidence for convergence stems from GO results. The experienced populations fed creosote share three ontologies (response to stimulus, oxidation-reduction process, lipid metabolic process), which all relate to biotransformation (Table 6).

Constitutive differences

While many biotransformation enzymes are induced when an animal is exposed to xenobiotics, some are expressed constitutively at high levels [31]. It is difficult to identify such baseline differences in expression using microarrays. For example, a recent study on an herbivorous insect that specializes on glucosinolate-rich plants did not identify any induced biotransformation transcripts when the insects were fed glucosinolates compared to a control diet [47]. Constitutive expression could explain this outcome. In our study, direct comparisons of gene expression between populations fed creosote provide insight into how animals differ in baseline biotransformation, especially when coupled with the results from the induction study. The experienced N. bryanti induce very few transcripts, only one of which has known biotransformation function, relative to both the naïve N. bryanti and the experienced N. lepida. However, direct comparisons of experienced N. bryanti with both the naïve conspecific and experienced congeneric when all are fed creosote, revealed many more differences in expression (Table 2A and B). Overall, the experienced N. bryanti had greater expression of significantly more biotransformation enzymes. This pattern coupled with the paucity of induced transcripts suggests that the experienced N. bryanti may be constitutively expressing biotransformation enzymes at a higher level. It is possible that N. bryanti’s longer historic exposure to creosote caused an increase in baseline production of biotransformation enzymes such that they continually express the appropriate combination of enzymes to efficiently detoxify creosote PSCs [22,23]. Moreover, the experienced N. lepida GO terms include many for regulation and signal transduction, suggesting processes in flux, whereas these terms are absent from the experienced N. bryanti results (Table 6).

Conclusions

Herbivores and the plants on which they feed represent one of the most common interactions in nature, yet we know relatively little about the mechanisms that herbivores, particularly mammalian ones, employ to overcome plant toxins [1,48]. The application of recently developed genome-based approaches is enabling researchers to more thoroughly investigate the responses of herbivores to plant defensive compounds. This work capitalized on the availability of a recently developed microarray to identify the genes induced by mammalian herbivores when feeding on PSCs. The results lay the requisite groundwork for future functional and evolutionary studies of the genes involved in the metabolism of creosote toxins and the evolution of diet switching in woodrats.

Methods

Trapping and feeding trial

We trapped two species, N. lepida (desert woodrat) and N. bryanti (Bryant’s woodrat). Neotoma lepida were trapped at Lytle Ranch Preserve (lat: 37.117514, long: -114.009661, Washington Co., UT, USA). Neotoma bryanti were trapped near Palm Springs (lat: 33.679616 long: -116.362018, Riverside Co., CA, USA). These two populations were chosen because both the desert woodrat and Bryant’s woodrat at these sites include creosote bush (L. tridentata) as a primary component of their diet [35] (unpublished observations by MDD and JRM). With respect to creosote ingestion, we refer to these populations as “experienced,” both in their individual histories as well as their evolutionary histories. In preliminary trials, experienced animals from both species were capable of ingesting high levels of creosote resin (8% by dry mass) added to a powdered rabbit chow base (Teklad formula 2031). In addition, we trapped N. bryanti at Ronald W. Caspers Wilderness Park (lat: 33.53367, long: -117.54965, Orange Co., CA, USA). This population has no evolutionary or ecological exposure to creosote bush, and is considered “naïve” to creosote PSCs. In preliminary trials, these animals did not maintain body mass on diets of 4% creosote resin. All experimental procedures were approved by the University of Utah’s Institutional Animal Care and Use Committee (#07-02015).

Eight woodrats from each of the three groups (experienced N. lepida, experienced N. bryanti, naïve N. bryanti) were divided into two treatments of four individuals (n = 2 males, 2 females). One treatment was fed powdered rabbit chow amended with resin from creosote bush; the other group was fed a control diet of the same powdered rabbit chow with no additions. Resin was extracted and creosote diets prepared as in [34].

Animals given the resin diet were fed a gradually increasing amount of resin over an eight-day period to allow induction of biotransformation enzymes [31]. This group received powdered chow with 0% resin for three days, 1% creosote resin (dw/dw) for two days, followed by 2% creosote resin for three days. The final 2% concentration was selected to accommodate the naïve N. bryanti since they were unable to tolerate more resin without excessive mass loss (>10% initial weight). Animals in the control treatments received 0% resin diet for all eight days. Animals had water ad libitum, and diet was presented daily. Animals were weighed daily and body masses were compared within and between groups using a repeated measures ANOVA with time as the repeated variable and population and diet as factors.

Animals were dispatched using CO2 asphyxiation; liver tissue was preserved in RNAlater (Sigma) and archived at -80°C. RNA was extracted (RNAqueous) for the microarray analysis.

Microarray analysis

Liver samples were analyzed using a custom microarray, built from the hepatic transcriptome of a single desert woodrat [36]. Two primary probe groups were designed from the transcriptome. The target contigs for the first group (n = 943) were woodrat contigs whose annotation matched a list of biotransformation genes extracted from Norway rat arrays that we had previously used in studies with woodrats [34,49]. These probes were all labeled “biotransformation.” The target contigs in the second group consisted of contigs from the woodrat transcriptome that had ≥75% sequence identity with a rodent BLAST match in the region of highest homology (n = 5355). All probes were screened for quality and replicated on the array.

The RNA quality and concentration of each sample was evaluated, and the Agilent One-Color Quick Amp Labeling Kit was used to generate fluorescently labeled cRNA for hybridizations. Additional details on microarray processing methods are available in [36]. Microarray features were extracted using Agilent Feature Extraction software version 10.5.1.1. All control spots, non-uniform spots and population outlier spots were removed from the dataset; intensity values were log2 transformed using AgilentFilter, software designed to simplify the processing of Agilent data. Data from duplicate probes were combined, but different probes with the same annotation were maintained separately since it is possible that the original contigs were from different isoforms despite the shared match to a rodent gene. Consequently, many of the resulting lists of differentially expressed genes have multiple seemingly identical entries. For most analyses, we treat these probes as targeting unique genes; in a few specified analyses, we have combined or discarded duplicate probes to evaluate the results as conservatively as possible. The performance of the custom Neotoma expression array was previously validated [36].

Species and diet comparisons

To compare gene expression across diet and species, the data for the Neotoma probes was batch uploaded to Genesifter 3.7. Prior to comparing expression profiles, the consistency of transcriptome response was evaluated by comparing overall gene expression profiles across individuals. After normalizing the intensity data, individuals were clustered by gene expression using all woodrat-derived probes (n = 6286). Clustering parameters were distance:correlation, linkage:average, row centered:by genes.

We created a total of five pairwise comparisons in Genesifter. The specific nature of these comparisons are described in the subsequent paragraphs. In all comparisons, the quality requirement was set to 1, and all individuals from both treatments were required to pass. T-tests were performed with alpha = 0.05, and resulting lists of significantly differentially expressed genes/probes were ordered by fold change with a fold change threshold of greater or equal to 2. This approach is less conservative than implementing a statistical control for the false discovery rate (e.g., Benjamini and Hochberg correction [50]), but fold change ranking is more consistent [51].

To identify induction and repression of genes with respect to ingestion of resin, we compared expression on the creosote diet to the control diet for each of the three groups (experienced N. lepida, experienced N. bryanti, naïve N. bryanti). The lists of significantly differently expressed genes were ordered by direction and fold change. Transcripts that were upregulated on the creosote diet were considered induced by creosote and may be indicative of enzymes important in the biotransformation of creosote. Transcripts that were downregulated were considered repressed. To test for conserved or convergent responses, the lists of induced genes were compared for entries present in more than one woodrat group.

In the fourth comparison, naïve and experienced N. bryanti fed the creosote diet, were compared to identify contrasts in expression with respect to prior experience. Using the gene lists generated from these comparisons, we compared the overall number of transcripts with greater expression in each group as well as the subset of these transcripts characterized by having biotransformation function. The standard gene lists treat probe entries with identical Genbank accession numbers as independent listings. To more conservatively compare the relative response of each group to the creosote diet, we quantified the number of unique Genbank accessions in the biotransformation gene lists and, then calculated the Shannon’s H Diversity Index from each list. To calculate Shannon’s H, each unique Genbank accession was treated as a “species” and the number of times it appeared in the significantly upregulated list was treated as its “abundance”. The values for Shannon’s H were then used to calculate an effective number of upregulated genes i.e., the number of “species” expected in comparable communities given their Shannon’s H. This index is used to contextualize diversity indices across multiple communities [52]. The effective species value (or effective gene value, in this case) is calculated as exp (H).

To examine function more broadly, we used Gene Ontology (GO). GO is a bioinformatics tool that groups individual genes by the function of their products. GO allows the organization of many individual gene results into fewer functionally-defined categories. There are 3 major classifications: cellular component, molecular function and biological process. Within each of these three, function is categorized more and more specifically. Within our GO results, z-scores were used to determine significantly important associations. Ontology terms with z-scores of >2 are considered to be significantly overrepresented in the results; that is, the genes in that ontology are more likely to be upregulated than expected by chance, given the number features on the array within that particular GO term. Within the biological process classification, two gene ontology lists were generated for transcripts with greater expression in naïve N. bryanti and in experienced N. bryanti. Lastly, experienced animals from both species fed the creosote diet were compared to illuminate contrasts in expression between species with similar experience. This contrast was conducted in the same fashion as the naïve versus experienced N. bryanti.

Abbreviations

PSC: Plant secondary compounds; NDGA: Nordihydroguiairetic acid; GO: Gene ontology; AKR: Aldo-keto reductase; UGT: UDP glucuronosyltransferase.

Competing interests

The authors declare that they have no competing interests.

Authors’ contributions

JRM: Performed the experiments, analyzed the data, contributed to manuscript draft; MSS: Contributed to the analysis and interpretation; MDD: Designed the study, obtained funding and contributed to manuscript draft, contributing equally with JRM. All authors contributed substantially to manuscript revisions. All authors read and approved the final manuscript.

Supplementary Material

Additional file 1: Table S1

Animal masses before and after feeding trial.

Click here for file (28.5KB, xls)
Additional file 2: Figure S1

Cluster analysis of individual woodrat samples labeled by treatment. Description: Branching pattern determined by overall gene expression patterns. Individual animals are labelled with species and experience with creosote bush in the wild; creosote diet in laboratory trial is indicated by bolded text.

Click here for file (103.9KB, pdf)
Additional file 3: Table S2

Significantly differently expressed transcripts from comparison of naïve versus experienced N. bryanti. Description: (A.) Transcripts with greater expression by naïve N. bryanti; (B.) transcripts with greater expression by experienced N. bryanti. All animals were fed a creosote diet. Duplicates indicate the response of multiple probes for a given gene.

Click here for file (94.5KB, xls)
Additional file 4: Table S3

Significantly differently expressed transcripts from comparison of experience N. byranti versus experienced N. lepida. Description: (A.) Transcripts with greater expression by N. bryanti; (B.) transcripts with greater expression by N. lepida. All animals were fed a creosote diet. Duplicates indicate the response of multiple probes for a given gene.

Click here for file (69KB, xls)

Contributor Information

Jael R Malenke, Email: malenke@biology.utah.edu.

Michele M Skopec, Email: micheleskopec@weber.edu.

M Denise Dearing, Email: denise.dearing@utah.edu.

Acknowledgements

We would like to thank K. Kohl, A. Fitzgerald, and J. Varner for help with the woodrats and B. Milash in the U. U. Microarray Core for assistance. NSF (IOS 0817527 and 1256383) provided funding.

References

  1. Dearing MD, Foley WJ, McLean S. The influence of plant secondary metabolites on the nutritional ecology of herbivorous terrestrial vertebrates. Ann Rev Ecology Evolution Systematics. 2005;36:169–189. doi: 10.1146/annurev.ecolsys.36.102003.152617. [DOI] [Google Scholar]
  2. Foley WJ, McArthur C. In: The Digestive System in Mammals: Food, Form and Function. Chivers DJ, Langer P, editor. Cambridge: Cambridge University Press; 1994. The effects and costs of allelochemicals for mammalian herbivores: an ecological perspective; pp. 370–391. [Google Scholar]
  3. Berenbaum MR. Postgenomic chemical ecology: from genetic code to ecological interactions. J Chem Ecol. 2002;28:873–896. doi: 10.1023/A:1015260931034. [DOI] [PubMed] [Google Scholar]
  4. Skopec MM, Haley SL, Dearing MD. Differential gene expression in the livers of a dietary specialist versus generalist species of woodrat. Integr Comp Biol. 2004;44:641. [Google Scholar]
  5. Vaughn TA. Stephen’s woodrat, a dietary specialist. Jour Mammal. 1982;63:53–62. doi: 10.2307/1380671. [DOI] [Google Scholar]
  6. Westoby M. What are the biological bases of varied diets. Amer Natur. 1978;112(985):627–631. doi: 10.1086/283303. [DOI] [Google Scholar]
  7. Dearing MD, McLister JD, Sorensen JS. Woodrat (Neotoma) herbivores maintain nitrogen balance on a low-nitrogen, high-phenolic forage, Juniperus monosperma. J Comp Physiol B. 2005;175:349–355. doi: 10.1007/s00360-005-0491-3. [DOI] [PubMed] [Google Scholar]
  8. Freeland WJ, Janzen DH. Strategies in herbivory by mammals the role of plant secondary compounds. Amer Natur. 1974;108(961):269–289. doi: 10.1086/282907. [DOI] [Google Scholar]
  9. Li XC, Schuler MA, Berenbaum MR. Molecular mechanisms of metabolic resistance to synthetic and natural xenobiotics. Ann Rev Entomol. 2007;52:231–253. doi: 10.1146/annurev.ento.51.110104.151104. [DOI] [PubMed] [Google Scholar]
  10. Matzkin LM, Watts TD, Bitler BG, Machado CA, Markow TA. Functional genomics of cactus host shifts in Drosophila mojavensis. Mol Ecol. 2006;15:4635–4643. doi: 10.1111/j.1365-294X.2006.03102.x. [DOI] [PubMed] [Google Scholar]
  11. Ishizuka M, Okajima F, Tanikawa T, Min H, Tanaka KD, Sakamoto KQ, Fujita S. Elevated warfarin metabolism in warfarin-resistant roof rats (Rattus rattus) in Tokyo. Drug Metab Dispos. 2007;35(1):62–66. doi: 10.1124/dmd.106.011775. [DOI] [PubMed] [Google Scholar]
  12. Despres L, David JP, Gallet C. The evolutionary ecology of insect resistance to plant chemicals. Trends Ecol Evol. 2007;22(6):298–307. doi: 10.1016/j.tree.2007.02.010. [DOI] [PubMed] [Google Scholar]
  13. Croft D, O’Kelly G, Wu G, Haw R, Gillespie M, Matthews L, Caudy M, Garapati P, Gopinath G, Jassal B, Jupe S, Kalatskaya I, Mahajan S, May B, Ndegwa N, Schmidt E, Shamovsky V, Yung C, Birney E, Hermjakob H, D’Eustachio P, Stein L. Reactome: a database of reactions, pathways and biological processes. Nucleic Acids Res. 2011;(Database issue):D691–D697. doi: 10.1093/nar/gkq1018. [DOI] [PMC free article] [PubMed] [Google Scholar]
  14. Pratt WB, Taylor P. In: Principles of Drug Action: the Basis of Pharmacology. 3. Pratt WB PT, editor. New York, New York, USA: Churchill Livingstone Inc; 1990. Principles of drug action the basis of pharmacology third edition; p. 836. [Google Scholar]
  15. Ellegren H, Sheldon BC. Genetic basis of fitness differences in natural populations. Nature. 2008;452:169–175. doi: 10.1038/nature06737. [DOI] [PubMed] [Google Scholar]
  16. King MC, Wilson AC. Evolution at two levels in humans and chimpanzees. Science. 1975;188:107–116. doi: 10.1126/science.1090005. [DOI] [PubMed] [Google Scholar]
  17. Fraser HB. Gene expression drives local adaptation in humans. Genome Res. 2013;23:1089–1096. doi: 10.1101/gr.152710.112. [DOI] [PMC free article] [PubMed] [Google Scholar]
  18. Lopez-Maury L, Marguerat S, Bahler J. Tuning gene expression to changing environments: from rapid responses to evolutionary adaptation. Nat Rev Genet. 2008;9:583–593. doi: 10.1038/nrg2398. [DOI] [PubMed] [Google Scholar]
  19. Whitehead A, Crawford DL. Variation within and among species in gene expression: raw material for evolution. Mol Ecol. 2006;15:1197–1211. doi: 10.1111/j.1365-294X.2006.02868.x. [DOI] [PubMed] [Google Scholar]
  20. Hunter KL, Betancourt JL, Riddle BR, Van Devender TR, Cole KL, Spaulding WG. Ploidy race distributions since the Last Glacial Maximum in the North American desert shrub, Larrea tridentata. Global Ecol Biogeography. 2001;10:521–533. [Google Scholar]
  21. Patton JL, Huckaby DG, Álvarez-Castañeda ST. The Evolutionary History and a Systematic Revision of the Woodrats of the Neotoma lepida Group. Berkeley: University of California Press; 2008. [Google Scholar]
  22. Spaulding WG. In: Packrat Middens: The Last 40,000 years of Biotic Change. Betancourt JL, Van Devender TR, Martin PS, editor. Tuscon: University of Arizona Press; 1990. Vegetational and climatic development of the Mojave Desert: The last glacial maximum to the present; pp. 166–199. [Google Scholar]
  23. Van Devender TR. In: Packrat Middens: The Last 40,000 years of Biotic Change. Betancourt JL, Van Devender TR, Martin PS, editor. Tuscon: University of Arizona Press; 1990. Late-Quaternary vegetation and climate of the Sonoran Desert, United States and Mexico; pp. 134–165. [Google Scholar]
  24. Adams RP, Zanoni TA, Von Rudloff E, Hogge L. The southwestern USA and northern Mexico one seeded junipers their volatile oils and evolution. Biochem Systemat Ecol. 1981;9:93–96. doi: 10.1016/0305-1978(81)90025-9. [DOI] [Google Scholar]
  25. Holchek JL, Munshikpu AV, Nunez-Hernandez G, Valdez R, Wallace JD, Cardenas M. Influences of six shrub diets varying in phenol content on intake and nitrogen retention by goats. Tropical Grasslands. 1990;24:93–98. [Google Scholar]
  26. Hodgkinson A. Oxalic Acid in Biology and Medicine. New York, NY: Academic Press; 1977. [Google Scholar]
  27. Mabry TJ, Difeo DRJ, Sakakibara M, Bohnstedt CFJ, Seigler D. In: Creosote Bush Biology and Chemistry of Larrea in New World Deserts. vol. 6. Mabry TJ, Hunziker JH, Difeo DR, editor. New York, NY: Academic Press; 1977. The natural products chemistry of Larrea; pp. 115–134. [Google Scholar]
  28. Goodman T, Grice HC, Becking GC, Salem FA. A cystic nephropathy induced by nordihydroguaiaretic acid in the rat: light and electron microscopic investigations. Lab Invest. 1970;23:93–107. [PubMed] [Google Scholar]
  29. Grice HC, Becking G, Goodman T. Toxic properties of nordihydroguaiaretic acid. Food Cosmet Toxicol. 1968;6:155–161. doi: 10.1016/0015-6264(68)90197-1. [DOI] [PubMed] [Google Scholar]
  30. Shneeman BO, Azarnoff DL, Christiansen CL, Clark AM, Farnsworth NR, Gansler T, Gibson JE, Goldman SA, Guzelian PS, Jeffrey E, Koller LD, Lau J, Molyneux RJ, Percival SS, Rock CL, Ward JM. Review of Liver-Related Risks for Chaparral. Washington DC: The National Academy of Sciences; 2004. Dietary Supplements: A Framework for Evaluating Safety. [Google Scholar]
  31. Klaassen CD. Cararett and Doull’s Toxicology: The Basic Science of Poisons. New York: McGraw Hill; 2001. [Google Scholar]
  32. Haley SL, Lamb JG, Franklin MR JEC, Dearing MD. Pharm-ecology of diet shifting: Biotransformation of plant secondary compounds in creosote (Larrea tridentata) by a woodrat herbivore, Neotoma lepida. Physiol Biochem Zool. 2008;81:584–593. doi: 10.1086/589951. [DOI] [PubMed] [Google Scholar]
  33. Magnanou E, Malenke JR, Dearing MD. Hepatic gene expression in herbivores on diets with natural and novel plant secondary compounds. Physiol Genomics. 2013;45:774–785. doi: 10.1152/physiolgenomics.00033.2013. [DOI] [PubMed] [Google Scholar]
  34. Magnanou E, Malenke JR, Dearing MD. Expression of biotransformation genes in woodrat (Neotoma) herbivores on novel and ancestral diets: identification of candidate genes responsible for dietary shifts. Mol Ecol. 2009;18:2401–2414. doi: 10.1111/j.1365-294X.2009.04171.x. [DOI] [PubMed] [Google Scholar]
  35. Mangione AM, Dearing MD, Karasov WH. Interpopulation differences in tolerance to creosote bush resin in desert woodrats (Neotoma lepida) Ecology. 2000;81:2067–2076. doi: 10.1890/0012-9658(2000)081[2067:IDITTC]2.0.CO;2. [DOI] [PubMed] [Google Scholar]
  36. Malenke JR, Milash B, Miller AW, Dearing MD. Transcriptome sequencing and microarray development for the woodrat (Neotoma spp.): custom genetic tools for exploring herbivore ecology. Mol Ecol Resour. 2013;13:674–687. doi: 10.1111/1755-0998.12092. [DOI] [PubMed] [Google Scholar]
  37. Haley SL, Lamb JG, Franklin MR, Constance JE, Dearing MD. Xenobiotic metabolism of plant secondary compounds in oak (Quercus agrifolia) by specialist and generalist woodrat herbivores, genus Neotoma. J Chem Ecol. 2007;33:2111–2122. doi: 10.1007/s10886-007-9371-5. [DOI] [PubMed] [Google Scholar]
  38. Haley SL, Lamb JG, Franklin MR, Constance JE, Denise M. Xenobiotic metabolism of plant secondary compounds in juniper (Juniperus monosperma) by specialist and generalist woodrat herbivores, genus Neotoma. Comp Biochem Physiol C Toxicol Pharmacol. 2007;146:552–560. doi: 10.1016/j.cbpc.2007.06.007. [DOI] [PubMed] [Google Scholar]
  39. Pass GJ, McLean S, Stupans I, Davies N. Microsomal metabolism of the terpene 1,8-cineole in the common brushtail possum (Trichosurus vulpecula), koala (Phascolarctos cinereus), rat and human. Xenobiotica. 2001;31(4):205–221. doi: 10.1080/00498250110043535. [DOI] [PubMed] [Google Scholar]
  40. Pass GJ, McLean S, Stupans I, Davies NW. Microsomal metabolism and enzyme kinetics of the terpene p-cymene in the common brushtail possum (Trichosurus vulpecula), koala (Phascolarctos cinereus) and rat. Xenobiotica. 2002;32(5):383–397. doi: 10.1080/00498250210124138. [DOI] [PubMed] [Google Scholar]
  41. Zhang L, Jin Y, Huang M, Penning TM. The role of human aldo-keto reductases in the metabolic activation and detoxication of polycyclic aromatic hydrocarbons: Interconversion of PAH catechols and PAH o-quinones. Front Pharmacol. 2012;3:193. doi: 10.3389/fphar.2012.00193. [DOI] [PMC free article] [PubMed] [Google Scholar]
  42. Barski OA, Tipparaju SM, Bhatnagar A. The aldo-keto reductase superfamily and its role in drug metabolism and detoxification. Drug Metab Rev. 2008;40:553–624. doi: 10.1080/03602530802431439. [DOI] [PMC free article] [PubMed] [Google Scholar]
  43. Mangione AM, Dearing D, Karasov W. Detoxification in relation to toxin tolerance in desert woodrats eating creosote bush. J Chem Ecol. 2001;27:2559–2578. doi: 10.1023/A:1013639817958. [DOI] [PubMed] [Google Scholar]
  44. Arteaga S, Andrade-Cetto A, Cardenas R. Larrea tridentata (Creosote bush), an abundant plant of Mexican and US-American deserts and its metabolite nordihydroguaiaretic acid. J Ethnopharmacol. 2005;98:231–239. doi: 10.1016/j.jep.2005.02.002. [DOI] [PubMed] [Google Scholar]
  45. Singh S, Brocker C, Koppaka V, Chen Y, Jackson BC, Matsumoto A, Thompson DC, Vasiliou V. Aldehyde dehydrogenases in cellular responses to oxidative/electrophilic stress. Free Radic Biol Med. 2013;56:89–101. doi: 10.1016/j.freeradbiomed.2012.11.010. [DOI] [PMC free article] [PubMed] [Google Scholar]
  46. Vasiliou V, Pappa A, Petersen DR. Role of aldehyde dehydrogenases in endogenous and xenobiotic metabolism. Chem Biol Interact. 2000;129:1–19. doi: 10.1016/S0009-2797(00)00211-8. [DOI] [PubMed] [Google Scholar]
  47. Whiteman NK, Gloss AD, Sackton TB, Groen SC, Humphrey PT, Lapoint RT, Sonderby IE, Halkier BA, Kocks C, Ausubel FM, Pierce NE, Pierce NE. Genes involved in the evolution of herbivory by a leaf-mining Drosophilid fly. Genome Biol Evol. 2012;4(9):900–916. doi: 10.1093/gbe/evs063. [DOI] [PMC free article] [PubMed] [Google Scholar]
  48. Whiteman NK, Jander G. Genome-enabled research on the ecology of plant-insect interactions. Plant Physiol. 2010;154(2):475–478. doi: 10.1104/pp.110.161117. [DOI] [PMC free article] [PubMed] [Google Scholar]
  49. Skopec MM, Haley S, Dearing MD. Differential hepatic gene expression of a dietary specialist (Neotoma stephensi) and generalist (Neotoma albigula) in response to juniper (Juniperus monosperma) ingestion. Comp Biochem Physiol D-Genomics & Proteomics. 2007;2:34–43. doi: 10.1016/j.cbd.2006.11.001. [DOI] [PubMed] [Google Scholar]
  50. Benjamini Y, Hochberg Y. Controlling the false discovery rate: a practical and powerful approach to multiple testing. Jour Royal Stat Soc. 1995;57:289–300. Series B. [Google Scholar]
  51. Guo L, Lobenhofer EK, Wang C, Shippy R, Harris SC, Zhang L, Mei N, Chen T, Herman D, Goodsaid FM, Hurban P, Phillips KL, Xu J, Deng X, Sun YA, Tong W, Dragan YP, Shi L. Rat toxicogenomic study reveals analytical consistency across microarray platforms. Nat Biotechnol. 2006;24:1162–1169. doi: 10.1038/nbt1238. [DOI] [PubMed] [Google Scholar]
  52. Jost L. Entropy and diversity. Oikos. 2006;113:363–375. doi: 10.1111/j.2006.0030-1299.14714.x. [DOI] [Google Scholar]

Associated Data

This section collects any data citations, data availability statements, or supplementary materials included in this article.

Supplementary Materials

Additional file 1: Table S1

Animal masses before and after feeding trial.

Click here for file (28.5KB, xls)
Additional file 2: Figure S1

Cluster analysis of individual woodrat samples labeled by treatment. Description: Branching pattern determined by overall gene expression patterns. Individual animals are labelled with species and experience with creosote bush in the wild; creosote diet in laboratory trial is indicated by bolded text.

Click here for file (103.9KB, pdf)
Additional file 3: Table S2

Significantly differently expressed transcripts from comparison of naïve versus experienced N. bryanti. Description: (A.) Transcripts with greater expression by naïve N. bryanti; (B.) transcripts with greater expression by experienced N. bryanti. All animals were fed a creosote diet. Duplicates indicate the response of multiple probes for a given gene.

Click here for file (94.5KB, xls)
Additional file 4: Table S3

Significantly differently expressed transcripts from comparison of experience N. byranti versus experienced N. lepida. Description: (A.) Transcripts with greater expression by N. bryanti; (B.) transcripts with greater expression by N. lepida. All animals were fed a creosote diet. Duplicates indicate the response of multiple probes for a given gene.

Click here for file (69KB, xls)

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