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  • Mark Christie

    2019

  • 2

    TABLE OF CONTENTS Page

    I. GENERAL INFORMATION ...........................................................................................................................4 A. Education.......................................................................................................................................................4 B. Previous Positions .........................................................................................................................................4 C. Present Position .............................................................................................................................................4 D. Awards and Honors .......................................................................................................................................4 E. Professional and Scholarly Associations ......................................................................................................4

    II. LEARNING ........................................................................................................................................................5 A. Teaching Assignments at Purdue ..................................................................................................................5

    B. Selected Discussion of Courses ....................................................................................................................6 C. Course Evaluation .........................................................................................................................................8

    1. Student ...................................................................................................................................................8 D. Other Teaching Experience ...........................................................................................................................9 E. Other Contributions to Undergraduate Education ..........................................................................................9

    III. DISCOVERY ....................................................................................................................................................10 A. Discussion of Research ...............................................................................................................................10 B. Publications .................................................................................................................................................20

    1. Refereed ...............................................................................................................................................20 2. In Press .................................................................................................................................................20 3. Submitted .............................................................................................................................................23 4. In Preparation .......................................................................................................................................24 5. Book Chapters ......................................................................................................................................24 6. Book Chapters in Press ........................................................................................................................24 7. Book Reviews/Editorials .....................................................................................................................24 8. Abstracts ..............................................................................................................................................24

    C. Invited Lectures...........................................................................................................................................24 1. National and International Meetings ....................................................................................................24 2. Regional Meetings and Workshops .....................................................................................................25 3. Universities and Other Institutions ......................................................................................................25

    D. Other Presented Papers ...............................................................................................................................26 E. Other Professional Activities ......................................................................................................................27 F. Interdisciplinary Activities ..........................................................................................................................27 G. Patents .........................................................................................................................................................27 H. Funding .......................................................................................................................................................27

    1. Discussion of Support ..........................................................................................................................27 2. Funding ................................................................................................................................................27

    I. Evidence of Involvement in Graduate Research Program ..........................................................................29 1. Number of M.S. and Ph.D. Students Graduated ..................................................................................29 2. Current Graduate Students, Post doctorates, and Undergraduates ......................................................29

    IV. ENGAGEMENT ............................................................................................................................................... 30 A. Discussion of Service .................................................................................................................................. 30 B. Department .................................................................................................................................................. 30 C. College of Science....................................................................................................................................... 30 D. University .................................................................................................................................................... 30 E. Professional ................................................................................................................................................. 31

    1. Grant Review ....................................................................................................................................... 31 2. Editorial Board ..................................................................................................................................... 31 3. Reviewed Manuscripts ......................................................................................................................... 31 4. Reviewed Grants for agencies ............................................................................................................. 31 5. Contacted and participated on grant panels.......................................................................................... 31

    F. Diversity Activities ..................................................................................................................................... 31

    G. Other Engagement Activities ...................................................................................................................... 31 V. APPENDIX ....................................................................................................................................................... 34

    A. Appendix A – Your 3 Year Plan .................................................................................................................34

    B. Appendix B – Mentoring Section ..................................................................................................…….

  • 3

    C. Appendix C – Open Discussion on Work with Undergraduates............................................................. D. Appendix D – Free Response Area.........................................................................................................

  • 4

    I. GENERAL INFORMATION

    A. Education 2009 Ph.D., Zoology, Oregon State University - Corvallis, OR.

    2002 B.A., Biology, Cum Laude, Boston University - Boston, MA.

    B. Previous Positions

    2012-2014 Postdoctoral Research Fellow: University of Michigan, Ann Arbor, MI.

    Genetic effects of habitat connectivity on long-term population persistence;

    emphasis on modeling and Approximate Bayesian Computation.

    L. Lacey Knowles advisor

    2010-2014 Postdoctoral Research Fellow: Oregon State University, Corvallis, OR.

    Research on the effects of salmon hatcheries on wild populations.

    Michael S. Blouin advisor

    2003-2009 Research Assistant: Oregon State University, Corvallis, OR.

    Research on the dispersal and recruitment of marine fishes.

    Mark A. Hixon advisor

    2004-2005 Field Assistant: Lee Stocking Island, Bahamas.

    Assisted with ongoing sampling and experiments of coral-reef fish ecology.

    2002-2003 Research Associate: Exact Sciences Biotech, Boston, MA.

    Performed molecular work to optimize novel genetic approaches for diagnosing

    cancer.

    2001-2002 Research Assistant: New England Aquarium, Boston, MA.

    1999-2002 Research Assistant: Boston University Marine Program and Marine Biological

    Laboratory, Woods Hole, MA.

    C. Present Position 2014-Present Assistant Professor, Department of Biological Sciences & Department of Forestry

    and Natural Resources, Purdue University, West Lafayette, IN

    D. Awards and Honors

    E. Professional and Scholarly Associations

    American Genetic Association

    American Society of Ichthyologists and Herpetologists

    Ecological Society of America

    International Society of Computational Biology

    Society for the Study of Evolution

    Western Society of Naturalists

  • 5

    II. LEARNING

    A. Teaching Assignments at Purdue (Written by Candidate)

    Semester Year Course # Title, Credit, Type Enroll. Student

    Classification

    Fall 2015 FNR 241 Ecology & Systematics of

    Fishes, 3 credits

    84 Undergraduate

    Spring 2016 BI 58000 Evolution, 3 credits

    18 Senior/Graduate

    Spring 2016 BI 65300 Advanced Evolution Discussion, 1 credit

    7 Graduate

    Spring 2016 BI 59500 Genomics in Ecology and Evolution, 1 credit

    9 Graduate

    Fall 2016 FNR 24150 Ecology & Systematics of Fishes, 3 credits

    87 Undergraduate

    Fall 2016 BI65200 Advanced Ecology & Evolution Discussion, 1 credit

    11 Graduate

    Spring 2017 BI 58000 Evolution, 3 credits

    21 Undergraduate & Graduate

    Spring 2017 BI 69500 Writing in Ecology & Evolution, 1 credit

    6 Graduate

    Fall 2017 FNR 24150 Ecology & Systematics of Fishes, 3 credits

    81 Undergraduate

    Fall 2017 BI65200 Advanced Ecology & Evolution Discussion, 1 credit

    4 Graduate

    Spring 2018 BI 58000 Evolution, 3 credits

    37 Undergraduate & Graduate

    Spring 2018 BI 69500 Writing in Ecology & Evolution, 1 credit

    4 Graduate

    Fall 2018 FNR 24150 Ecology & Systematics of Fishes, 3 credits

    93 Undergraduate

    Spring 20019 BI 58000 Evolution, 3 credits

    32 Undergraduate & Graduate

  • 6

    B. Selected Discussion of Courses (Written by Candidate)

    FNR24150

    The ecology and systematics of fishes and herptiles provides a general overview of two dominant

    vertebrate taxa. The course is a requirement for all Forestry and Natural Resource students and

    enrollment in some years can exceed 90 students. Most students taking the class are sophomores.

    I teach the fishes portion of this course (1/2 semester) for fulfillment of my 25% appointment in

    the Department of Forestry and Natural Resources. This course is rewarding, but it is a challenge

    to present an overview of all 33 thousand extant fishes within half a semester. As such, I mainly

    focus on broad phylogenetic relationships and draw upon examples from specific species

    throughout. When I arrived at Purdue, this course was taught with hierarchical, taxonomic

    relationships. I quickly transitioned to using modern phylogenetic relationships among fishes,

    which simultaneously requires students to understand phylogenetic methods and to understand

    the evolutionary relationships among an immensely diverse group of vertebrates. For many

    students, this course is their first exposure to evolution.

    Because of time constraints, this course mostly focuses on extant species. The course

    begins with jawless fishes (agnathans), moves on to chimaeras, sharks, and rays

    (Chondrichthyes), and then progresses to bony fishes (Osteichthyes). Within the osteicthyes we

    focus on Sarcopterygii and the evolution of terrestrial vertebrates before spending a considerable

    portion of the class reviewing the diversity found within the ray finned fishes (Actinopterygii).

    Beyond the phylogenetic relationships, I also provide an overview of swimming mechanics,

    ectothermy (and regional endothermy), respiration, osmoregulation, buoyancy, sensory systems,

    schooling, feeding ecology & behavior, reproduction, early life history, growth, population and

    community ecology, fish genetics, and conservation.

    I begin each class with a “Fish of the Day”,

    which features a fish that I find particularly

    interesting. We first review the phylogenetic

    placement of the fish (where does it fit in relation to

    other fishes) and then I present a suite of interesting

    facts about the fish. For example, south American

    leaf fish not only look like different stages of dead

    leaves (figure 1), individuals act like dead leaves too

    and use this camouflage to hunt prey and escape

    predation. I also use “think-pair-share” activities in

    every lecture, where I propose a big picture, often

    conceptual question, ask the students to talk it over

    with their neighbors for 1-2 minutes, and then ask

    Figure 1: South American leaf fish (Monocirrhus polyacanthus) look and act like dead and decaying leaves.

    for volunteers to present their answers. Because the questions are largely conceptual, there is

    often no one correct or incorrect answer. The students quickly realize that there is little risk with

    offering unusual answers and participation in this portion of the lecture is considerably higher

    then I expected when I first trialed this activity. The student’s creativity in their answers have in

    many cases resulted in diverse solutions to complex problems – such that I have started writing

    many of them down for further exploration. Lastly, I include lots of short videos showing fishes

    in their natural environments – many of these videos focus on marine fishes and it is rewarding

    to watch the students’ eyes opened to entirely new worlds.

  • 7

    BIO58000

    “Nothing in biology makes sense except in the light of evolution” - Theodosius Dobzhansky

    “Nothing in evolution makes sense except in the light of population genetics” - Michael Lynch

    Evolution is the only upper level evolution course offered at Purdue University. This course

    introduces students to fundamental and advanced concepts in evolutionary biology including

    population genetics, natural selection, genetic adaptation, and speciation. Because nothing in

    evolution makes sense except in the light of population genetics, each semester is begun with a

    comprehensive introduction to this field. Population genetics has a rich mathematical history, but

    I find that simply presenting a series of equations, while illuminating for some students, leaves

    the vast majority of students confused or completely in the dark. Consequently, I have developed

    a comprehensive set of individual-based models that illustrate each of the four fundamental

    evolutionary forces that affect allele frequencies: genetic drift, mutation, gene flow, and natural

    selection (figure 2). Each

    module is written in R and

    because enrollment in this

    class is capped at 30 students,

    we can use the 16

    departmental laptops to allow

    students to work in class in

    groups of two. Parameters are

    set at the beginning (i.e., the

    top) of each script and include

    variables such as population

    size, initial allele frequency,

    mortality rate etc. The code

    for each of the modules is

    appended below the

    parameters and, for extra

    credit, I allow students to

    modify the code to identify

    answer questions the

    presented model cannot (e.g., Figure 2: Screen shot illustrating one of the R modules designed to illustrate the effects of genetic drift. Each point represents an individual and each color represents the allele of that individual. Allele frequencies can be identical at the start of the simulation (a shown here) or varied by the student along with carrying capacity, number of offspring per pair, and dispersal strategy.

    responses at multiple, linked

    loci). All of the code is

    available on our lab website

    and our lab GitHub repository.

    After obtaining an introduction in population genetics, the course moves on to cover topics

    in domestication, rapid evolution, microevolution, speciation, sexual selection, life history

    evolution, and phenotypic evolution. We also discuss the role and application of genomics and

    bioinformatics to modern evolutionary analyses. Because this course convenes for 75 minutes

    twice per week, I typically lecture for the first 30-40 minutes and then spend the remainder of the

    class time with active learning activities. Aside from working with R scripts we discuss relevant

    papers as a class, present figures from papers to the class (in groups of 4-5), design theoretical

  • 8

    experiments in small groups, review papers on bioRxiv, present on evolution in the news, and

    work with new bioinformatics software.

    I find the large amounts of group work undertaken in this course to be particularly

    enjoyable. When groups of 2-5 students are working together I always walk around and provide

    feedback and additional information when needed; it is particularly rewarding to hear students

    coming up with novel questions, unique experimental designs, and problem-solving strategies.

    When I first took over this course, the format consisted of straightforward lecturing with time for

    occasional questions. While I think this strategy was effective for some students, the gradual

    transition to a highly interactive classroom has been one of my most rewarding teaching

    accomplishments. Future development will include greater exposure of students to coding,

    refinement of lecture material, and the continued trialing and implementation of various active

    learning exercises.

    C. Course Evaluation

    Evaluations of past courses are summarized below. Two values are reported for courses that

    contained two sections. “Course” refers to answers to the prompt, “Overall, I would rate this

    course as,” while “instructor” refers to answers to the prompt, “Overall, I would rate this

    instructor as.” These values are out of a possible score of 5 where 5 = ‘Excellent’, 4 = ‘Good’,

    3=’Fair’, 2=’Poor”, and 1 = ‘Very Poor’.

    Fall 2015: FNR24150

    Course: 4.0

    Instructor: 3.9

    Spring 2016: BI 58000

    Course: 4.1

    Instructor: 4.2

    Fall 2016: FNR 24150

    Course: 4.3

    Instructor: 4.0

    Spring 2017: BI 58000

    Course: 3.8

    Instructor: 4.3

    Fall 2017: FNR 24150

    Course: 4.5

    Instructor: 4.3

    Spring 2018: BI 58000

    Course: 4.1 (mode 4)

    Instructor: 4.6 (mode 5)

    Fall 2018: FNR 24150

  • 9

    Course: 4.3 (mode 4)

    Instructor: 4.4 (mode 4)

    D. Other Teaching Experience:

    Guest Lectures:

    Survey of Mathematical Biology (BTNY 560) Purdue University 2018

    Fish and Wildlife Forensics (FNR 59800) Purdue University (West Lafayette, IN) 2017

    Demystifying Mathematical Models (BTNY 590) Purdue University 2017

    Fish and Wildlife Forensics (FNR 59800) Purdue University (West Lafayette, IN) 2016

    Fish and Wildlife Forensics (FNR 59800) Purdue University (West Lafayette, IN) 2015

    Evolution (BIOL 58000) Purdue University (West Lafayette, IN) 2015

    Freshman Honors Biology Seminar (BI 19700) Purdue University 2015

    Evolution (EEB 516) University of Michigan (Ann Arbor, MI) 2013

    Ecology (BI 370) Oregon State University (Corvallis, OR) 2011

    Ichthyology (FW 315) Oregon State University (Corvallis, OR) 2009-2011

    Marine Ecology (Z352) Oregon State University (Corvallis, OR) 2005-2007

    Graduate Teaching Instructor 2002-2009

    Marine Ecology

    Oregon State University (Corvallis, OR)

    - lead lectures for recitations and laboratories (including field trips)

    (Z352, 2 terms, 24 students)

    Introductory Biology (BI 212, 2 terms, 4 sections, 200 students)

    Oregon State University (Corvallis, OR)

    lead lectures for recitations and laboratories

    Vertebrate Zoology (BI 302, 2 sections, 84 students)

    Boston University (Boston, MA)

    lead laboratory sections

    Workshops, Oregon State University (Corvallis, OR) 2008

    Center for Genome Resources and Biocomputing

    R Workshop for Statistical Computing

    E. Other Contributions to Undergraduate Education

  • 10

    Completed mentoring one honors undergraduate, Abigail Perkins, who conducted

    independent research on the sea lamprey project. She is currently employed at IUPUI as a

    research associate. Two additional undergraduate students have now also joined the lab

    and are working on projects related to bioinformatics and experimental design.

    Mentored two undergraduate biology majors during the 2014-2015 school year. Each

    student completed an independent research project.

    III. DISCOVERY

    A. Discussion of Research (Written by Candidate)

    Our planet is changing at an unprecedented pace and scale with large impacts to terrestrial and

    aquatic ecosystems. For example, global climate change is creating widespread and often

    extreme environmental changes that will have profound impacts on ecological communities.

    Entire ecosystems, such as coral-reefs, are in severe peril due to increasing temperatures, rising

    water levels, and ocean acidification all of which are triggered by changing climatic conditions

    (figure 1), and recent studies have suggested that coral-reefs may go extinct within the next 30-

    50 years. With such large-scale and high-impact environmental changes, ecologists and

    evolutionary biologist are faced

    with a pressing question: Can

    species adapt to rapid

    environmental change? This

    single question is the central focus

    of my research program because

    the answers will guide future

    conservation and management

    actions for the next generation. If a

    species cannot keep pace with Figure 1: Healthy reef-building acroporid coral (left photo) versus colonies of bleached corals (right photo). High water temperatures, which cause corals to expel their symbiotic algae required for photosynthesis, in combination with rising water levels and increased ocean acidification are threatening coral reef ecosystems.

    projected environmental changes,

    then extinction is the likely

    outcome in the absence of direct

    intervention (e.g., captive

    breeding).

    Understanding which species can rapidly adapt to novel environmental changes and how

    they are able to adapt may allow us to better predict which species can be managed in situ. Given

    that a response to selection requires a heritable trait, it may be that some genomic properties are

    good predictors of adaptive ability; genome-wide estimates of genetic diversity, recent genome

    duplication events, and areas of high recombination all represent possible predictors of adaptive

    ability. The power of and promise of genetic tools is high, but much more work needs be

    accomplished before we can begin to build a predictive framework for understanding which

    species can adapt to environmental change.

    To that end, my research focuses three themes related to whether species can keep pace

    with rapid environmental change and all three themes focus on genetic adaptation to novel

    conditions: 1. rapid genetic adaptation of introduced species to novel environments, 2. rapid

  • 11

    genetic adaptation to xenobiotic compounds, and 3. rapid genetic adaptation to captivity.

    Although I often focus on the outcomes of selection, additional evolutionary forces, such as

    genetic drift and gene flow feature prominently in these three themes. My work has primarily

    focused on fishes, but is largely question driven and thus focused on diverse taxa ranging from

    schistosomes to southern right whales and banner-tailed kangaroo rats.

    1: Rapid genetic adaptation of introduced species to novel environments.

    Understanding how introduced species can adapt to novel environments provides a useful

    framework for understanding adaptive evolution because in many cases species are predicted to

    have large shifts in their geographic ranges outside of their current, native boundaries.

    Work in my lab has focused on two non-native species - the introduced steelhead trout

    (Oncorhynchus mykiss; figure 2) and the invasive sea lamprey (Petromyzon marinus; figure 5) -

    both of which now occur in the Laurentian Great Lakes. The Great Lakes are an ideal location

    for studying rapid genetic adaptation to novel environments due to the diverse habitats and

    relatively recent colonization events for most non-native species.

    Steelhead trout are an ecologically, economically, and culturally important fish that are

    native to the northern Pacific and surrounding regions. Steelhead exhibit an extraordinary

    amount of life history variation both within and among populations. In fact, two alternative life

    history variants - the ocean-going, anadromous steelhead and the stream-residing resident

    rainbow trout - are so phenotypically divergent that they were once classified as separate species

    (figure 2), though my work and others have established that these life history variants routinely

    interbreed with one another. In fact, two freshwater resident fish can produce ocean-going

    steelhead progeny and vice versa (Christie et al. 2011). There is also extensive life history

    variation within just the ocean-going, anadromous steelhead. Some steelhead are semelparous;

    they spawn once and die. Semelparous steelhead may return to spawn at different ages (2-5 years

    old), spending various amounts

    of time in freshwater or marine

    habitats. Other steelhead, known

    as repeat spawners or kelts,

    spawn two and sometimes three

    times in their lifetime, returning

    to the ocean between each

    spawning event. Furthermore,

    some steelhead mature in the

    ocean before returning to rivers

    to spawn (e.g., winter-run

    steelhead), while others return

    early and overwinter in

    Figure 2: Mature resident male O. mykiss (top) next to an ocean-

    returning steelhead male (bottom). Ocean-going males are considerably larger than their resident counterparts. In the Great Lakes, only the larger steelhead phenotype is documented. Photo courtesy of J. McMillan.

    freshwater before spawning (e.g.,

    summer-run steelhead). Recent

    work in my lab has revealed that

    many of these distinct life history

    strategies are maintained by a

  • 12

    Figure 3: Comparison of pooled heterozygosity (HP) across chromosomes and between populations. Mean HP,

    averaged across 25 100 kb windows, is illustrated by the solid lines. The 95% confidence interval around each mean is illustrated with shading

    combination of fitness trade-offs, where a fitness benefit associated with one function (e.g., size

    at reproduction) is correlated with a fitness cost of another function (e.g., survivorship) and

    negative frequency dependent selection, where the relative fitness of a particular life history

    strategy declines as the life history strategy increases in frequency (Christie et al. 2018).

    Both steelhead and rainbow trout, have been widely introduced throughout the world. In

    the late 1890s, steelhead from northern California were introduced into Lake Michigan and

    natural reproduction was documented shortly thereafter. In their native range, most steelhead

    spend the first one to two years of their lives in freshwater streams before migrating out to the

    ocean to forage and grow. By contrast, steelhead from Lake Michigan continue to spawn in

    streams and rivers, but now use the entirely freshwater environment of the Great Lakes as a

    surrogate ocean. Furthermore, there is no known interbreeding between resident and anadromous

    life history variants in Lake Michigan (i.e., steelhead and resident rainbow trout are not, to our

    knowledge, sympatric), suggesting that steelhead have adapted to the novel freshwater

    environment. Apart from salinity, there are many additional differences between the introduced

    and native habitats including water temperature, stream characteristics, and community

    composition. Beginning in the mid-1980s, hatchery fish of diverse ancestry were released into

    Lake Michigan, and their high survival rates allowed for possible introgression with the original,

    California-derived strain. To examine the genetic effects of this introduction, we sequenced the

    entire genomes of 264 fish using fish collected from the ancestral range in California, fish from

    Lake Michigan in the early 1980’s (before the possible hatchery introgression), and fish from the

    late 1990’s (after hatchery introgression) (Willoughby et al. 2018).

    In all three populations, genetic diversity was lowest at the centromeres and contained a

    region with extremely high heterozygosity on chromosome 5 (Figure 3), subsequently identified

    as an inversion associated with an anadromous life history in steelhead. When making

    comparisons between the California population and the Lake Michigan samples we found three

    striking patterns (Figure 3): First, heterozygosity in the ancestral California population was

  • 13

    Figure 4: SNPs and functions associated with the outlier region on chromosome 4. A) FST for all SNPs located within the outlier region, denoted by the extent of the black bracket, for both California vs. Lake Michigan 1983 and California vs. Lake Michigan 1998. Highlighted regions display the extent of the two genes located within the outlier region: 1. gram domain containing 4 (GRAMD4); and 2. ceramide kinase (CERK). (B) For all SNPs with large allele frequency changes found within CERK, we compared allele frequency of the major allele in the 1983 Lake Michigan population between the California, Lake Michigan 1983, and Lake Michigan 1998 populations. Many SNPs show evidence of positive selection favoring a previously rare allele, including 5 SNPs that resulted in non- synonymous changes (orange lines). The orange box displays the function of CERK: a kinase that phosphorylates ceramide, forming ceramide-1-phosphate (C-1-P), which then activates DNA synthesis, cell division, and wound-repair pathways. In both A and B, each short vertical, black line depicts the location of a single exon within the gene.

    higher than heterozygosity in the Lake

    Michigan across all chromosomes. In fact,

    Lake Michigan 1983 steelhead were

    characterized by a 9.5% reduction in

    genetic diversity across the entire genome.

    Second, we found that average

    heterozygosity in the 1998 Lake Michigan

    population was higher than heterozygosity

    in the 1983 Lake Michigan population,

    resulting in a mean 4.8% increase in

    genetic diversity between 1983 and 1998,

    a pattern which reflects the successful

    introgression of hatchery-stocked smolts.

    Lastly, we observed that the reduction in

    heterozygosity in the Lake Michigan

    populations relative to California

    depended on position along each

    chromosome. This pattern was not driven

    by changes in the total number of SNPs,

    read depth, occurrence of paralogous loci,

    gene density, or number of repetitive

    elements. Thus, the present-day

    distribution of genetic diversity in Lake

    Michigan steelhead likely reflects the

    evolutionary interplay among gene flow

    (here introgression from hatchery strains),

    recombination, and purifying selection.

    By examining genes in regions with

    high genetic differentiation between the

    California and Lake Michigan population,

    we found evidence of selection in

    osmoregulatory and acid-base balancing

    pathways on two independent

    chromosomes. We also found evidence of

    selection that altered metabolic processes

    were associated with the genetic

    adaptation of steelhead to the Great Lakes

    (Figure 4). The selection on CERK and

    the associated modulation of C-1-P

    induced cell proliferation suggests

    steelhead metabolism played an important

    role in adaptation to the freshwater

    environment. This adaptation may have

    allowed steelhead to take advantage of

    alternative prey or allocate additional

    resources to activity in the Lake Michigan habitat. Intriguingly, C-1-P greatly increases the DNA

  • 14

    synthesis of fibroblasts, cells that play a key role in wound healing pathways (Gomez-Muñoz et

    al., 1995, 1997; Singer & Clark, 1999). In the Great Lakes specifically, introduced, parasitic sea

    lamprey occur at high densities, and lamprey attacks result in large wounds resulting in mortality

    rates of ~40% parasitized O. mykiss individuals. Most lamprey species that exist in the native

    steelhead range are non-parasitic and parasitic Pacific lamprey occur at much lower densities

    than Lake Michigan sea lamprey and do not rely heavily on salmon as hosts. Thus, we speculate

    that C-1-P mediated wound healing may be a response to the strong selective pressure imposed

    by introduced parasitic sea lamprey found at high abundances in Lake Michigan. Future work in

    my lab will investigate the possibility of rapid coevolution between introduced steelhead and

    invasive sea lamprey.

    By comparing Lake Michigan steelhead to their ancestral population, we were able to

    uncover genomic patterns of rapid genetic adaptation to the Great Lakes ecosystem despite a

    reduction in genome-wide genetic diversity. That genetic adaptation can still occur despite

    genome-wide reductions in genetic diversity has substantial conservation and management

    implications; imperiled species with small population sizes may still be able to adapt to changing

    environmental conditions. Using genomic approaches to better understand which genes,

    populations, and species can rapidly respond to novel and often anthropogenically-induced

    selective forces represents a key component of future of conservation research.

    2. Rapid genetic adaptation to xenobiotic compounds

    The rapid evolution of resistance to xenobiotic compounds has been widely documented in

    microbes, fungi, invertebrates, and plants. Resistance has also been documented in vertebrates

    but has largely been constrained to taxa with high fecundity and short generation times.

    Nevertheless, the fundamental principles governing the evolution of resistance still apply to

    species with longer generation times. If the selection pressure imposed by a xenobiotic is strong,

    wide-spread, and consistently applied year after year, then resistance may still evolve. One such

    possibility occurs throughout the Great Lakes, where a powerful chemical lampricide has been

    applied to control invasive sea lamprey (Petromyzon marinus) for over 60 years. Because the

    lampricide kills most, but not all, larval sea lamprey, it is possible that some individuals are able

    to survive exposure. If this process is repeated over a long enough period, then resistant

    individuals could increase in frequency – a scenario documented in many systems where pests

    have been controlled by chemical means. The evolution of resistance would greatly reduce the

    effectiveness of the lampricide, which remains the primary control agent, and could result in

    Figure 5: Larval stage sea lamprey (Petromyzon marinus), known as ammocoetes, do not have functional eyes and remain buried in the substrate before transforming into parasitic adults. The parasitic adults use their circularly- arrayed teeth to attach to host fishes. The two photos of ammocoetes were taken by an undergraduate journalism/biology double major, Scott See, who worked in our lab.

  • 15

    large declines to native fish populations due to increases in lamprey abundance. These declines

    in fish abundance would not only have large ecological repercussions but could also result in

    billions of dollars in economic damage.

    Invasive sea lamprey impact native populations and communities by wounding and often

    killing the host fishes that they parasitize. Following their invasion into the Laurentian Great

    Lakes (hereafter Great Lakes) in the late 1930s, sea lamprey contributed to the catastrophic loss

    of economically valuable commercial and recreational fisheries in Canada and the United States.

    In response to the proliferation of sea lamprey throughout the Great Lakes, there was an

    immediate and concerted effort to develop efficient means of control. One effort, initiated in the

    1950s, involved testing over 6,600 chemical compounds on sea lamprey and other fish species.

    The organic compound 3-trifluoromethyl-4-nitrophenol (hereafter TFM) was found to effectively

    kill larval sea lamprey and had few detectable effects on other fish species at low concentrations.

    TFM control was highly successful and sea lamprey abundance was reported to have been

    reduced by approximately 90%, resulting in recovery of economically important fisheries. This

    outcome is one of the few documented cases of an invasive vertebrate species being successfully

    controlled by a pesticide. Alternative control measures have been implemented on smaller scales,

    but none have proven as effective as TFM. Thus, there is a continued reliance on TFM to

    manage invasive sea lamprey

    populations in the Great

    Lakes. This reliance on a

    single control measure can be

    risky; only a handful of

    manufacturers produce TFM

    (because the only known

    application is as a lampricide)

    and thus both prices and

    supplies of TFM could change

    (Dunlop et al. 2017). More

    importantly, reliance on a

    single chemical control

    measure has been shown in

    other pests to drastically

    increase the chances of

    resistance evolution.

    Figure 5: Effects of costs of resistance on the evolution of resistance. Panels A and B illustrate the relationship between the cost of resistance and the number of resistant larvae through time. TFM treatment was started in year 50 (black vertical line), a single resistant adult was added in year 70 (blue vertical line) and TFM treatment was stopped in year 100 (red vertical line). When there is no cost of resistance (panel A), the number of resistant larvae does not decline through time even after TFM treatment is stopped. When cost of resistance is moderate (10% reduction in fitness, panel B), the number of resistant larvae gradually declines through time. Panel C illustrates the proportion of resistant larvae as a function of years until detection where cost of resistance was varied from 0 to 0.5 (see legend). Panel D illustrates the trade-off between the proportion of parasites killed by TFM and the probability of resistance evolving examining three costs of resistance (colors match the legend in panel C).

    In order to determine

    when resistance is likely to

    evolve and to examine the

    factors that can expedite or

    delay the onset of resistance,

    we constructed an eco-genetic

    model that mimics the unique

    life history of sea lamprey

    (Figure 5). We found that

    resistance alleles rapidly rise

    to fixation after 40-80 years of

  • 16

    treatment. The absence of natal homing allows resistant individuals to spread quickly throughout

    the entire system making detection challenging while simultaneously increasing the overall

    likelihood of resistance evolving. High costs of resistance and density independent reproduction

    can delay, but not prevent, the onset of resistance (Figure 5). The results of this research

    illustrate that sea lamprey have the potential to evolve resistance to their primary control agent in

    the near future, highlighting the urgent need for alternative control strategies.

    In my lab we often combine theoretical work with empirical work. Towards the empirical

    end we have performed extensive toxicology and gene expression work on larval lamprey from

    their introduced and native ranges. We obtained a total of 1451 live sea lamprey (Petromyzon

    marinus) ammocoetes collected from three locations: 1. Lake Michigan, 2. Lake Champlain, 3.

    Connecticut. Lake Michigan has been treated with TFM for 59 years, Lake Champlain for 32

    years, and Connecticut for 0 years (native range). Larvae were acclimatized for a minimum of

    four months before the first exposure to TFM to minimize environmental effects.

    We found no differences in survivorship between larvae from the native range and larvae

    from TFM-treated portions of the range after exposure to TFM. However, we did detect large

    differences in gene expression between individuals exposed to sub-lethal concentrations of TFM

    where 197 genes were differentially expressed (most of which were upregulated) in larvae

    collected from Lake Michigan with only 5 and 13 genes differentially expressed in Connecticut

    and Lake Champlain, respectively, suggesting a different response among populations (Figure 6).

    We are currently in the process of identifying the pathways and specific functions of these 197

    genes, but these data suggest that Lake Michigan lamprey may have evolved resistance to

    sublethal exposure to TFM and may be in the initial stages of evolving lethal resistance.

    Functionally, most of

    the genes are involved

    in increasing the

    production of ATP,

    which validates the

    previously confirmed

    mode of action for

    TFM. To further

    confirm these

    preliminary results,

    we have just finished

    sequencing 56 more

    samples consisting of

    29 muscle tissue, 19

    liver tissue, and 8

    brain tissue.

    Figure 6: Patterns of gene expression between sea lamprey larvae exposed to sub- lethal concentrations of the lampricide TFM in comparison to control (unexposed) larvae from the same populations. A total of 197 genes were differentially expressed in larvae from Lake Michigan in comparison to 5 from Lake Champlain and 13 from Connecticut, suggesting a different response among populations

    3. Rapid genetic adaptation to captivity

    Captive environments are often strikingly different than those found in the wild. As such,

    understanding how species can rapidly adapt to captivity can provide insights into how and why

    rapid genetic adaptation occurs. Additionally, if species cannot adapt to changing environmental

    conditions captive breeding programs may represent a last resort. Thus, one goal of captive

    breeding programs is to bolster threatened or endangered populations. Yet these programs often

  • 17

    produce individuals that are maladapted upon reintroduction into the wild. Captive breeding on a

    massive scale is exemplified by the more than six billion hatchery-raised salmon that are

    intentionally released each year into the Northern Pacific ecosystem. I am currently leading a

    multidisciplinary project to investigate the genetic impacts of releasing hatchery steelhead

    (Oncorhynchus mykiss) into the wild. Despite having wild-origin fish as parents, it was unclear

    why hatchery fish had substantially lower reproductive success in the wild than their wild-born

    counterparts. To address this unknown, I reconstructed pedigrees for three generations of fish

    (13,000 fish from 15 years), and determined that hatchery fish were unexpectedly adapting to the

    captive environment in a single generation. These results demonstrate that a single generation

    in captivity can result in a substantial response to selection on traits that are beneficial in

    captivity, but severely maladaptive in the wild (Christie et al. (2012b), PNAS; highlighted in

    NPR, NY Times, and Faculty of 1000). This finding of rapid genetic adaptation represents a

    general phenomenon found in many first-generation hatchery salmon species and populations,

    and thus has major implications for the viability of threatened fish populations (Christie et al.

    2014).

    My salmon research is also uncovering complex tradeoffs that arise with any

    supplementation and captive breeding program. For example, by combining novel pedigree and

    population genetic analyses, I was able to determine that supplementation programs can reduce

    the effective population size of an entire population by nearly two-thirds (Christie et al. 2012a).

    This work on hatcheries also revealed that the loss in genetic diversity was greatest when (1)

    more hatchery fish were allowed onto the spawning grounds and (2) the reproductive success of

    returning hatchery fish was high. These findings suggest that explicitly accounting for the

    demographic, genetic, and societal costs and benefits of supplementation could pave the way for

    more prudent management actions. Recent theoretical work in my lab has addressed the long-

    term demographic and genetic effects associated with releasing captive-born individuals with

    varied life histories into the wild (Willoughby and Christie 2017, 2018). We developed eco-

    genetic models for four species with long-running captive-breeding and release programs: coho

    salmon (Oncorhynchus kisutch), golden lion tamarin (Leontopithecus rosalia), western toad

    (Anaxyrus boreas), and whooping crane (Grus americana). We found that releasing even slightly

    less fit captive-born individuals to supplement wild populations can result in reductions in

    population sizes and genetic diversity over the long term, provided that the fitness reductions are

    heritable (i.e., due to genetic adaptation to captivity) and that the populations continue to be

    regulated by density-dependent mechanisms. Species with longer life spans and lower rates of

    population replacement experienced smaller negative effects than those with shorter life spans

    and higher rates of population replacement. Furthermore, programs that released captive-born

    individuals over fewer years or that could avoid breeding individuals with captive ancestry

    experienced smaller reductions in population size and genetic diversity over the long term.

    Relying on selection in the wild to remove individuals with reduced fitness mitigated some

    negative demographic effects, but at a substantial cost to neutral genetic diversity. These recent

    results suggest that conservation-focused captive breeding programs should take measures to

    prevent even small amounts of genetic adaptation to captivity, quantitatively determine the

    minimum number of captive-born individuals to release each year, and fully account for the

    interactions among genetic adaptation to captivity, population regulation, and life history

    variation

    Ongoing work in this research area includes (1) determining the specific genes and traits

    that are under selection in the hatchery, (2) examining the ongoing role of life-history variation

  • 18

    in rapid genetic adaptation, and (3) determining whether the lack of mate choice in captivity can

    contribute to the production of offspring that have reduced fitness in the wild (e.g., inbreeding,

    sexual selection, MHC genes).

    Future work [work in progress – add yellow perch stuff; DNR stuff]

    Ongoing and future work in my lab focuses on each of the three broad topics discussed above.

    My lab is expanding our sea lamprey research to identify the timing and potential genetic

    mechanisms of resistance and to identify the rapid co-evolution among invasive sea lamprey and

    introduced salmonids. We are also expanding our study systems to identify further generalities of

    rapid genetic adaptation to novel environments. For example, we are examining rapid genetic

    adaptation to the Great Lakes with pink salmon, which have a well-documented progenitor

    population (samples obtained in collaboration with Lisa and Jim Seeb). We are also investigating

    the possibility of genetic adaptation to thiamine (vitamin B1) poor diets that afflict some salmon

    populations, which may become an emerging conservation issue. With increasing empirical

    observations of rapid adaptive evolution, occur our central aim is to develop a unified framework

    for contemporary evolution. Such a framework will be used to guide the ongoing conservation

    and management of threatened and imperiled populations.

    Literature cited:

    Christie, M. R., M. J. Ford, and M. S. Blouin. 2014. On the reproductive success of early‐

    generation hatchery fish in the wild. Evolutionary Applications 7:883-896.

    Christie, M. R., M. Marine, R. French, R. S. Waples, and M. Blouin. 2012a. Effective size

    of a wild salmonid population is greatly reduced by hatchery supplementation.

    Heredity 109:254.

    Christie, M. R., M. L. Marine, and M. S. Blouin. 2011. Who are the missing parents?

    Grandparentage analysis identifies multiple sources of gene flow into a wild

    population. Molecular Ecology 20:1263-1276.

    Christie, M. R., M. L. Marine, R. A. French, and M. S. Blouin. 2012b. Genetic adaptation

    to captivity can occur in a single generation. Proceedings of the National

    Academy of Sciences 109:238-242.

    Christie, M. R., G. G. McNickle, R. A. French, and M. S. Blouin. 2018. Life history

    variation is maintained by fitness trade-offs and negative frequency-dependent

    selection. Proceedings of the National Academy of Sciences:201801779.

    Dunlop, E. S., R. McLaughlin, J. V. Adams, M. Jones, O. Birceanu, M. R. Christie, L. A.

    Criger, J. L. Hinderer, R. M. Hollingworth, and N. S. Johnson. 2017. Rapid

    evolution meets invasive species control: the potential for pesticide resistance in

    sea lamprey. Canadian Journal of Fisheries and Aquatic Sciences 75:152-168.

    Willoughby, J. R., and M. R. Christie. 2017. Captive Ancestry Upwardly Biases

    Estimates of Relative Reproductive Success. Journal of Heredity 108:583-587.

  • 19

    Willoughby, J. R., and M. R. Christie. 2018. Long‐term demographic and genetic

    effects of releasing captive‐born individuals into the wild. Conservation

    Biology.

    Willoughby, J. R., A. M. Harder, J. A. Tennessen, K. T. Scribner, and M. R. Christie.

    2018. Rapid genetic adaptation to a novel environment despite a genome‐wide

    reduction in genetic diversity. Molecular Ecology.

    B. Publications

    I have published in the following journals listed in order of the most recent impact factor (ISI

    Web of Knowledge): Nature Communications (11.6), Proceedings of the National Academy of

    Sciences USA (9.8), Molecular Ecology (6.3), Conservation Biology (5.9), Molecular Ecology

    Resources (5.6), Ecology (5.2), Evolution (4.7), Bioinformatics (4.6), Evolutionary Applications

    (4.6), PLoS Neglected Tropical Diseases (4.5), Heredity (3.8), PLoS One (3.5), Reviews in Fish

    Biology & Fisheries (3.2), Oecologia (3.1), ICES Journal of Marine Science (2.9), Canadian

    Journal of Fisheries and Aquatic Sciences (2.8), Ecology & Evolution (2.5) Marine Genomics

    (2.0) , Journal of Heredity (1.9), Environmental Biology of Fishes (0.914)

    Publications co-authored with undergraduate students, graduate students, and post-doctoral

    researchers are superscripted with U, G, and P, respectively. In the fields of ecology and

    evolution, the first and last author positions have the greatest significance, where first author

    typically denotes the individual who performed the majority of analytical work (e.g., data

    collection, data analysis) and the last author position denotes the individual whose lab the work

    came from. There are exceptions, particularly when all co-authors are professors (or similar), and

    cases in which I was the first author, but where the work originated from my lab are designated

    with an asterix (*). Text in blue font represents perspectives and coverage of the publication

    written by un-affiliated persons.

    1. Refereed

    34. Willoughby JRP, Waser PM, Brüniche-Olsen A, Christie MR (2019) Inbreeding load

    and inbreeding depression estimated from lifetime reproductive success in a small, dispersal-

    limited population. Heredity. In press.

    33. Harder AMG, Ardren WR, Evans AN, Futia MH, Kraft CE, Marsden JE, Richter CA,

    Rinchard J, Tillitt DE, Christie MR (2018) Thiamine deficiency in fishes: causes,

    consequences, and potential solutions. Reviews in Fish Biology and Fisheries 28:865-886.

    32. Martinez ASG, Willoughby JRP, Christie MR (2018) Habitat type and life history

    variation determine genetic diversity in fishes. Ecology and Evolution 8:12022-12031.

    31. Willoughby JRP, Christie MR. Long-term demographic and genetic effects of releasing

    captive-born individuals into the wild. Conservation Biology (In press).

    Perspective by Jake Buehler: “Releasing captive-bred animals has long-term drawbacks.”

    Frontiers in Ecology and the Environment 16(9):492-493.

  • 20

    30. Willoughby JRP, Harder AMG, Tennessen JA, Scribner KT, Christie MR (2018) Rapid

    genetic adaptation to a novel environment despite a genome-wide reduction in genetic

    diversity. Molecular Ecology 27:4041-4051.

    Perspective by Lisa Seeb, Garrent McKinney, and Jim Seeb: “Chromosomes and genes,

    spawned these fateful scenes: rapid adaptation in an introduced fish”. Molecular Ecology

    (In press).

    Highlighted in Science Magazine (AAAS): “This saltwater trout evolved to live in

    freshwater—in just 100 years.” doi:10.1126/science.aau3582.

    29. Johnson, DW, Christie MR, Pusack TJ, Stallings CD, Hixon MA (2018) Integrating

    larval connectivity with local demography reveals regional dynamics of a marine

    metapopulation. Ecology 99: 1419-1429.

    28. Christie MR*, McNickle GG, French RA, Blouin MS (2018) Life history variation is

    maintained by fitness trade-offs and negative frequency dependent selection. Proceedings of

    the National Academy of Sciences 115:4441-4446.

    27. Christie MR, Searle CL (2018). Evolutionary rescue in a host-pathogen system results in

    coexistence not clearance. Evolutionary Applications 11:681-693.

    26. Willoughby JRP, Christie MR (2017) Captive ancestry upwardly biases estimates of

    relative reproductive success in supplemented populations. Journal of Heredity 108:583-

    587.

    25. Christie MR*, Miermans PG, Gaggioti OE, Toonen RJ, White C (2017) Disentangling

    the relative merits and disadvantages of parentage analysis and assignment tests for inferring

    population connectivity. ICES Journal of Marine Science 74:1749-1762.

    Contribution to Themed Section: “Beyond ocean connectivity: new frontiers in early life

    stages and adult connectivity to meet assessment and management”.

    24. Dunlop, ES, McLaughlin R, Adams JV, Jones M, Birceanu O, Christie MR, Criger LA,

    Hinderer JLM, Hollingworth RM, Johnson NS, Lantz S, Li W, Miller J, Morrison BJ, Mota-

    Sanchez D, Muir A, Sepúlveda MS, Steeves T, Walter L, Westman E, Wirgin I, and Wilkie

    MP (2017) Rapid evolution meets invasive species control: The potential for pesticide

    resistance in sea lamprey. Canadian Journal of Fisheries and Aquatic Sciences. 75:152-

    168.

    23. Thompson NF, Christie MR, Marine ML, Curtis LD, Blouin MS (2016) Spawn date

    explains variation in growth rate among families of hatchery reared Hood River steelhead

    (Oncorhynchus mykiss). Environmental Biology of Fishes 99:581-591.

    22. Christie MR, Marine ML, Fox SE, French RA, Blouin MS (2016) A single generation of

    domestication heritably alters the expression of hundreds of genes. Nature Communications

    7:10676.

    21. Thomaz AT, Christie MR, Knowles LL (2016) The architecture of river networks can

    drive the evolutionary dynamics of aquatic populations. Evolution 70:731-739.

    20. Johnson DW, Christie MR, Stallings CD, Pusack TJ, Hixon MA (2015) Using post-

    settlement demography to estimate larval survivorship: a coral reef fish example. Oecologia

    179:729-739.

  • 21

    19. Christie MR, Knowles LL (2015) Habitat corridors facilitate genetic resilience

    irrespective of species dispersal abilities or population sizes. Evolutionary Applications.

    18. Christie MR, Ford MJ, Blouin MS (2014) On the reproductive success of early-

    generation hatchery fish in the wild. Evolutionary Applications 7: 883-896.

    17. Pusack TJ, Christie MR, Johnson DW, Stallings CD, Hixon MA (2014) Spatial and

    temporal patterns of larval dispersal in a coral-reef fish metapopulation: evidence of variable

    reproductive success. Molecular Ecology 23: 3396-3408.

    16. Fox S.E., Christie M.R., Marine M.L., Priest H.D., Mockler T.C., Blouin M.S. (2014)

    De novo sequencing and characterization of the anadromous steelhead (Oncorhynchus

    mykiss) transcriptome and its application for expression analyses in hatchery and wild fish.

    Marine Genomics 15: 13-15.

    15. Christie M.R., French R.A., Marine M.L., Blouin M.S. (2014) How much does

    inbreeding contribute to the reduced fitness of captive-born individuals in the wild? Journal

    of Heredity 105: 111-113.

    14. Christie M.R. (2013). Bayesian parentage analysis reliably controls the number of false

    assignments in natural populations. Molecular Ecology 22: 5731-5737.

    13. Christie M.R., Hixon M.A. (2013) Patterns of reef-fish larval dispersal in Exuma Sound,

    Bahamas in Coastal-Marine Conservation: Science and Policy (eds. G. Carleton Ray, J.

    McCormick-Ray), 2nd edition.

    12. Steinauer M.L., Christie M.R., Blouin M.S., Agola L.E., Mwangi I.N., Maina G.M.,

    Mutuku M.W., Kinuthia J.M., Mkoji G.M., Loker E.S. (2013). Kinship analysis reveals

    strong family structure in schistosome parasite samples from humans. PLoS Neglected

    Tropical Diseases 7: e2456.

    11. Christie M.R., Tennessen J.A., Blouin M.S. (2013) Bayesian parentage analysis with

    systematic accountability of genotyping error, missing data, and false matching.

    Bioinformatics 29: 725-732.

    10. Christie M.R., Marine M.L., French R.A., Blouin M.S. (2012) Genetic adaptation to

    captivity can occur in a single generation. Proceedings of the National Academy of Sciences

    109: 238-242.

    9. Christie M.R., Marine M.L., French R.A., Waples R.S., Blouin M.S. (2012) Effective size

    of a wild salmonid population is greatly reduced by hatchery supplementation. Heredity 109:

    254-260.

    8. Carrol E., Childerhouse S.J., Christie M.R., Lavery S., Patenaude N., Alexander A.,

    Constantine R., Steel D., Boren L., Baker C.S. (2012) Paternity assignment and demographic

    closure in the New Zealand southern right whale. Molecular Ecology 21: 3960-3973.

    7. Christie M.R., Marine M.L., Blouin M.S. (2011) Who are the missing parents?

    Grandparentage analysis identifies multiple sources of gene flow. Molecular Ecology 20:

    1263-1276.

    Perspective by Kenyon Mobley: “Grandfathering in a new era of parentage analysis”.

    Molecular Ecology 20:1080-1082.

  • 22

    6. Johnson D.W., Christie M.R., Moye J., Hixon M.A. (2011) Genetic correlations between

    adults and larvae in a marine fish: potential effects of fishery selection on population

    replenishment. Evolutionary Applications 4: 621-633.

    5. Christie M.R., Tissot B.N., Albins M.A., Beets J.P., Jia Y., Ortiz D.M., Thompson S.E.,

    Hixon M.A. (2010) Larval connectivity in an effective network of marine protected areas.

    PLoS ONE 5(12): e15715.

    Top 1% of most cited articles in PLoS ONE

    Perspective by Pete Mooreside: “Tiny larvae signal big potential for MPAs”. Frontiers in

    Ecology and Evolution 9:91

    Perspective by Daniel Cressey: “Plans for marine protection highlight science gap”.

    Nature 469 (146):13

    4. Johnson D.W., Christie M.R., Moye J. (2010) Quantifying evolutionary potential of

    marine fish larvae: Heritability, selection and evolutionary constraints. Evolution 64: 2614-

    2628.

    3. Christie M.R., Stallings C.D., Johnson D.W., Hixon M.A. (2010) Self-recruitment and

    sweepstakes reproduction amid extensive gene flow in a coral-reef fish. Molecular Ecology

    19: 1042-1057.

    Perspective by Dennis Hedgecock: “Determining parentage and relatedness from genetic

    markers sheds light on patterns of marine larval dispersal”. Molecular Ecology 19:845-

    847.

    2. Christie M.R. (2010) Parentage in natural populations: novel methods to detect parent- offspring pairs in large datasets. Molecular Ecology Resources 10: 115-128.

    1. Christie M.R., Eble J.A. (2009) Isolation and characterization of 23 microsatellite loci in

    the yellow tang, Zebrasoma flavescens (Pisces: Acanthuridae). Molecular Ecology

    Resources 9: 544-546.

    3. Submitted

    1. LaRue ESG, Emery NC, Briley L, Christie MR. Geographic variation in dispersal can facilitate adaptive evolution in response to climate change. Diversity and Distributions.

    2. Christie MR*, Dunlop ES, Sepúlveda MS. Invasive sea lamprey may soon become resistant to their primary control agent, 3-triflouromethyl-4-nitrophenol. Evolutionary

    Applications.

    4. In Preparation (manuscripts available upon request)

    1. Willoughby JR, Waser PM, Christie MR. Abiotic factors determine metapopulation fitness in a fully pedigreed population.

    2. Martinez AS, Willoughby JR, Harder AM, Sparks M, Sepúlveda MS, Christie MR. Experimental transcriptomics uncovers incipient resistance in invasive sea lamprey.

    3. Harder AM, Ardren WR, Christie MR. Within family variation in response to thiamine deficiency.

  • 23

    4. Yin X, Martinez AS, Willoughby JR, Harder AM, Sparks M, Sepúlveda MS, Christie MR. Pesticide resistance genes have rapidly increased in frequency in invasive sea lamprey.

    C. Invited Lectures

    1. National and International Meetings

    2018 Identifying physiological and transcriptional responses to 3-trifluoromethyl-4-nitrophenol

    in susceptible and tolerant species (Great Lakes Fishery Commission, Cleveland, Ohio)

    2017 Genomic evidence of rapid adaptation to novel environments (Redefining Darwinian

    Fisheries: Integrating the Diverse Roles of Evolution in Fisheries Sustainability

    Symposium, Annual Meeting of the American Fisheries Society, Tampa, Florida)

    2017 The ecological and genetic sustainability of fisheries and aquaculture (The United States

    Borlaug Fellows in Global Food Security program, Summer Institute for Global Food

    Security, West Lafayette, Indiana)

    2015 Hundreds of genes remain differentially expressed after a single generation of

    domestication (Genomics of Adaptation Symposium, 145th Annual Meeting of the

    American Fisheries Society, Portland, Oregon)

    2015 Genetic approaches to measuring larval dispersal. The 39th larval fish conference.

    (Vienna, Austria) (declined)

    2015 Larval Connectivity and Local Adaptation in Yellow Perch (Great Lakes Fishery

    Commission, Ann Arbor, Michigan)

    2015 Assessing the chemical resistance of sea lampreys (Petromyzon marinus) to TFM (Great

    Lakes Fishery Commission, Ann Arbor, MI)

    2012 Pacific Coast Steelhead Management Meeting, Pacific States Marine Fisheries

    Commission (Port Townsend, Washington) (declined)

    2011 Larval dispersal, population connectivity and the management of marine species,

    American Fisheries Society (Seattle, Washington)

    2011 Assessing the role of marine protected areas in restoring, sustaining, and enhancing

    fisheries, American Fisheries Society (Seattle, Washington)

    2010 Where are the missing parents? Grandparentage analyses identifies reproductively

    successful residualized hatchery fish. Pacific Coast Steelhead Management Meeting,

    Pacific States Marine Fisheries Commission (Redmond, OR)

    2010 European Society for Evolutionary Biology, 14th (Marseilles, France)

    Regional Meetings and Workshops

    2018 Assessing the resistance of sea lamprey to TFM (Sea Lamprey Control Board, Ann Arbor

    Michigan)

    2018 Genetic considerations of broodstock management (Indiana Department of Natural

    Resources, Lake Monroe, Indiana)

  • 24

    2016 Larval Connectivity and Local Adaptation in Lake Michigan Yellow Perch (Lake

    Michigan Technical Committee Meeting, Michigan City, Indiana)

    2. Universities and Other Institutions

    2018 Integrating larval connectivity with local demography reveals regional dynamics of a

    marine metapopulation (California Polytechnic State University, San Luis Obispo,

    California).

    2018 Rapid evolution in a changing world (Michigan State University, East Lansing,

    Michigan).

    2017 Rapid genetic adaptation to captivity causes reduced fitness in the wild (Eastern Illinois

    University, Charleston, Illinois)

    2016 Rapid adaptation to captivity causes reduced fitness in the wild (University of Colorado,

    Boulder, Colorado)

    2014 Larval dispersal, rapid adaptation, and the role of variable reproductive success (Indiana

    University Purdue University Indianapolis, Indiana)

    2014 Larval dispersal, rapid adaptation, and the role of variable reproductive success

    (University of Southern California, California)

    2014 On the role of rapid adaptation in reducing the fitness of early generation hatchery fish

    (University of Oregon, Oregon)

    2014 Larval dispersal and the role of variable reproductive success (Oregon Institute for

    Marine Biology, University of Oregon, Oregon)

    2014 Rapid adaptation and the genetics of populations (Purdue University, Indiana)

    2012 Novel genetic approaches reveal patterns of dispersal and rapid adaptation (Old

    Dominion University, Virginia)

    2012 Genetic adaptation to novel environments can occur on ecological and evolutionary

    timescales (University of Michigan, Michigan)

    D. Other Presented Papers

    1. National and International Meetings

    2017 Genomic evidence of rapid adaptation to a novel environment. Ecological Society of

    America (Portland, OR)

    2013 Rapid adaptation to captivity: evidence from pedigree and gene expression data. Society

    for the Study of Evolution (Snowbird, UT)

    2012 Rapid adaptation to captivity can occur on ecological timescales. Ecological Society of

    America (Portland, OR)

    2011 Causes of fitness decline in hatchery steelhead from the Hood River. American Fisheries

    Society (Seattle, WA)

    2010 Where are the missing parents? Grandparentage analyses identifies reproductively

    successful residualized hatchery fish. Society for the Study of Evolution (Portland, OR)

  • 25

    2009 Patterns of population connectivity in a coral-reef fish. American Society of Ichthyologists

    and Herpetologists (Portland, OR)

    2008 Patterns of population connectivity in a coral-reef fish. Western Society of Naturalists,

    (Vancouver, Canada)

    2008 Larval retention and population connectivity in two coral-reef fishes. International Coral

    Reef Symposium (Ft. Lauderdale, FL)

    2008 Parentage in natural populations. EVO-WIBO: Evolutionary biology in the Pacific

    Northwest (Port Townsend, WA)

    2007 Determining patterns of larval connectivity using genetic methods. Biology Graduate

    Student Symposium (Newport, OR)

    2007 What determines the number of fish in the sea? National Science Board (Oregon State

    University, OR)

    2006 Patterns of larval retention and connectivity in a coral-reef fish. Western Society of

    Naturalists (Redmond, WA)

    Christie lab presentations:

    2018 Harder AM, Ardren WR, Christie, MR. Impacts of thiamine deficiency on metabolic

    pathways and genetic influences on disease outcomes in Atlantic salmon (American

    Fisheries Society, Atlantic City, New Jersey)

    2018 Martinez AS, Willoughby JR, Christie, MR. Assessing the resistance of sea lamprey

    (Petromyzon marinus) to the lampricide 3-trifluromethy-4-nitrophenol (American

    Fisheries Society, Atlantic City, New Jersey)

    2018 Dice LM, Sparks MM, Christie MR (2018) Does Acclimatization Time Affect Response

    to Lampricide Exposure in Sea Lamprey (Petromyzon marinus)?* (American Fisheries

    Society, Atlantic City, New Jersey)

    2017 Harder AM, Ardren WR, Christie, MR. Overview of thiamine deficiency complex and

    identification of underlying genetic mechanisms (Annual Meeting of the International

    Association for Great Lakes Research, Detroit, Michigan)

    2017 Harder AM, Ardren WR, Christie MR. Overview of thiamine deficiency complex and

    identification of underlying genetic mechanisms (Purdue University Forestry and Natural

    Resources Fisheries and Aquatics Group Seminar)

    2017 Martinez AM, Perkins A., Sepúlveda, MS., Christie, MR. Assessing the evolution of

    resistance to lampricides in Great Lakes sea lamprey (Great Lakes Restoration Initiative -

    Occurrence and Effects of Contaminants of Emerging Concern Symposium, Annual

    Meeting Society of Environmental Toxicology and Chemistry North America North

    America, Minneapolis, Minnesota)

    2017 Willoughby JR, Tennessen JA, Scribner KT, Christie MR. Genomic evidence of rapid

    adaptation to a novel environment (Annual Meeting of the Society for the Study of

    Evolution, Portland, Oregon).

  • 26

    2017 Willoughby JR, Christie MR. Genome-wide founder effects and rapid genetic adaptation

    of Pacific steelhead to Lake Michigan (Forestry and Natural Resources Department

    Seminar, Purdue).

    2016 Willoughby JR, Christie MR. Captive breeding has long term demographic and genetic

    effects for wild populations (Annual Meeting of the Society for the Study of Evolution,

    Austin, Texas).

    2016 Willoughby JR, Christie MR. Measurement of conservation need: demographic criteria

    do not capture declines in genetic diversity (Ecolunch Series, Purdue).

    2016 LaRue EA, Christie MR, Emery NC. Incorporating geographic variation in dispersal to

    better predict a species distribution under climate change (EEB EcoLunch Series, Purdue)

    2016 LaRue EA, Christie MR, Emery NC. Incorporating geographic variation in dispersal in

    order to better predict a species' distribution under climate change (Annual Meeting of the

    Ecological Society of America. Ft. Lauderdale, Florida)

    2016 LaRue EA, Christie MR, Holland J, Emery NC. Incorporating geographic variation in

    dispersal in order to better predict species' distributions under climate change (Annual

    Meeting of the U.S. International Association of Landscape Ecology. Asheville, North

    Carolina)

    * Poster presentation; unless indicated all others were contributed talks

    2. Regional Meetings and Workshops

    2017 Christie MR, Genomic evidence of rapid adaptation to novel environments. Purdue Faculty

    Retreat (Four Winds, Indiana)

    3. Universities and Other Institutions

    E. Other Professional Activities

    F. Interdisciplinary Activities

    G. Patents

    H. Funding 1. Discussion of Support (Written by Candidate)

    Since arriving at Purdue, I have received a total of $455,000 of funding in external

    grant support from three separate awards. Two of the funded grants are for 3 years

    of support from the Great Lakes Fisheries Commission, an international advisory

    group that funds fisheries related research in the Great Lakes. The Great Lakes

    Fisheries Commission has been operational since 1954 and receives continual

    federal support from both Canada and the United States per the 1954 Convention

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    on Great Lakes Fisheries treaty. Given the proximity of Purdue to the Great Lakes

    and my lab’s ongoing research with Great Lakes fishes, I anticipate that the Great

    Lakes Fisheries Commission will be a reliable source of funding for my lab. My

    third grant award is an AgSeed grant that will allow our lab to collect data to

    submit to aquaculture grants with larger monetary values. I currently have four

    grant proposals currently under review ranging in value from $200,00 to $412,000.

    Given that research in my lab spans basic and applied fields in ecology, evolution,

    fisheries, and genetics, I anticipate securing funding from additional sources

    including the National Oceanic and Atmospheric Administration Sea Grant

    program, U.S. fish and wildlife service, and large non-profit agencies such as

    Conservation International.

    2. Funding

    Current Awards:

    1. Agency/Title of Grant: Great Lakes Fisheries Commission; Population connectivity and local adaptation in yellow perch (Perca flavescens).

    2. Duration of Funding: 3 years 2018-2020 3. Total amount of award: $200,000 4. Role: Principal Investigator

    co-PI Tomas O. Höök, Department of Forestry and Natural Resources

    (Purdue University)

    1. Agency/Title of Grant: AgSEED (Agricultural Science and Extension for Economic Development); Improving Indiana aquaculture and fisheries by

    sequencing and characterizing the genome of yellow perch (Perca flavescens).

    2. Duration of Funding: 1 year; 2018-2019 3. Total amount of award: $50,000 4. Your Role: Principal Investigator

    1. Agency/Title of Grant: Great Lakes Fisheries Commission; Assessing the resistance of sea lampreys (Petromyzon marinus) to the lampricide TFM

    2. Duration of Funding: 2016-2018 3. Total amount of award: $200,000 4. Role: Principal Investigator

    co-PI Maria S. Sepúlveda, Department of Forestry and Natural Resources

    (Purdue University)

    1. Agency/Title of Grant: Indiana Department of Natural Resources; Assessing the genetic diversity of muskellunge (Esox masquinongy)

    2. Duration of Funding: 2018-2019 3. Total amount of award: $5000 4. Role: Principal Investigator

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    1. Agency/Title of Grant: National Science Foundation; Evolutionary rescue in response to infectious disease: when will populations be rescued from

    pathogens?

    2. Duration of Funding: 2019-2021 3. Total amount of award: $401,363 4. Role: Co-PI

    Pending Awards (Under review, no award decision has been made):

    1. Agency/Title of Grant: Great Lakes Fisheries Commission; Identifying the

    mechanism and timing of sea lamprey resistance (Petromyzon marinus) resistance to TFM

    2. Duration of Funding: 2020-2022 3. Total amount of award: $349,000 4. Role: Principal Investigator

    1. Agency/Title of Grant: Great Lakes Fisheries Commission; Genetic and

    phenotypic basis for fishery-induced evolution in Lake Michigan yellow perch 2. Duration of Funding: 2020-2021 3. Total amount of award: $200,000 4. Role: Co-PI

    1. Agency/Title of Grant: National Science Foundation; Genetic structure and

    population connectivity in coastal marine systems 2. Duration of Funding: 2020-2023 3. Total amount of award: $412,000 4. Role: Collaborative Research; Co-PI

    Past Awards:

    1. Agency/Title of Grant: Thompson Coral-Reef Graduate Fellowship 2. Duration of Funding: 2 years 3. Total amount of award: $12,600 4. Your Role: Principal Investigator

    1. Agency/Title of Grant: Conservation International; Larval Connectivity and Fish Population Replenishment in a Network of Marine Management Areas for

    Tropical Aquarium Fisheries

    2. Duration of Funding: 2 years 3. Total amount of award: $54,451.00 4. Your Role: Co-Principal Investigator

    I. Evidence of Involvement in Graduate Research Program

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    1. Number of M.S. (1) and Ph.D. Students Graduated (1)

    Elizabeth LaRue, PhD. Date graduated: 7/29/2017

    Dissertation: “Geographic variation in dispersal traits of Cakile Enentula: Implications

    for the evolution of species range limits”

    2. Current Graduate Students (3), Post doctorates (2), and Undergraduates (3)

    Current Students Degree/

    Date

    Entered

    Past Students Date Graduated/

    Date Entered

    Major Professor:

    Morgan Sparks Ph.D. 2017 Elizabeth LaRue Ph.D. 2017/2012

    Avril Harder Ph.D. 2015 Alex Martinez M.S. 2018/2015

    Claire Schraidt M.S. 2018

    Chairperson, Ph.D. Examining Committee:

    Trevor Vannatta (Biological Sciences)

    Ph.D. 2015 Alyssa Gleichsner (Biological Sciences)

    Ph.D. 2017/2012

    Member, Committee:

    Samarth Marthur (Biological Sciences)

    Ph.D. 2016 Gina Dembski (IUPUI)

    Ph.D. 2017/2013

    Riley Rackliffe (FNR)

    Ph.D. 2016 Jennifer Serafin (FNR)

    M.S. 2017/2014

    Taylor Senegal (FNR)

    M.S. 2017 Laura Ploughe (Biological Sciences)

    Ph.D. 2018/2013

    Elizabeth Allmon (FNR)

    Ph.D. 2018 Jennifer Antonides (FNR)

    Ph.D. 2018/2013

    Joshua Kraft (Botany and Plant Pathology)

    Ph. D. 2019 Tim Malinich

    (FNR)

    Ph.D. 2019/2014

    Present Postdoctoral Research Associates: Former Research Associates: Xiaoshen Yin Janna Willoughby

    Present Undergraduates: Former Undergraduates:

    Truman Shanna Newman

    Helen Abigail Perkins

    Lindsey Dice

    Joseph Buckley Ashley Higdon

  • 30

    Lab awards:

    Alex Martinez:

    Ross Graduate Fellowship, 2015, $24,000

    Dr. P.T. Gilham Graduate Award, 2015, $3,000

    Lindsey Fellowship, 2017, $1,000

    Morgan Sparks:

    Frederick N Andrews Assistantship, 2017-2018, $48,000

    Rosenberg Graduate Award, 2017, $4,000

    Dr. P.T. Gilham Graduate Award, 2017, $3,000

    Janna Willoughby:

    Postdoctoral Scholar Fellowship, FNR Investments in Excellence Program, 2017-2018, $100,000

    Graduate School Travel Grants, 2016-2017, $1400.

    Avril Harder,

    Graduate School Summer Research Grant, Purdue University, 2017, $3300

    Robert Ricklefs Travel Award, Purdue University, 2017, $500

    Alton A. Lindsey Graduate Fellowship in Ecology, 2016, Purdue University, $1000

    Elizabeth LaRue,

    Purdue Research Foundation Research Grant, 2016, $22,000

    IV. ENGAGEMENT

    A. Discussion of Service I have reviewed manuscripts for 26 journals. Additionally, I actively seek outreach

    opportunities to engage with K-12 students and the public to share my work.

    B. Department EEB critical review convener 2017-2018

    PRF graduate student awards committee 2015-2016

    Undergraduate Honors Student Committee 2015-2018

    EcoLunch seminar organizer 2015

    Umbarger Review 2017

    Biological Sciences Focus Day 2017

    C. College of Science Joined faculty of Computational Life Sciences 2015

    Reviewer for Lynn Fellowships (Computational Life Sciences) 2016

    FNR postdoctoral scholar review committee 2017

    D. University

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    E. Professional

    1. Grant review (see below)

    2. Editorial board

    3. Reviewed Manuscripts for the following journals (include number of accepted requests).

    Behavioral Ecology and Sociobiology (1), Bioinformatics (3), BMC Evolutionary Biology

    (1), Bulletin of Marine Science (1), Canadian Journal of Fisheries and Aquatic Sciences (5),

    Diversity and Distributions (1), Ecology (5), Ecology and Evolution (1), Environmental

    Biology of Fishes (2), Evolutionary Applications (8), Functional Ecology (1), Heredity (5),

    Journal of Applied Ecology (2), Journal of Heredity (1), Journal of Marine Biology (1),

    Journal of Theoretical Biology (1), Marine and Freshwater Research (1), Marine Ecology

    Progress Series (8), Methods in Ecology and Evolution (1), Molecular Ecology (22),

    Molecular Ecology Resources (7), Nature Communications (2), Nature Ecology & Evolution

    (3), PeerJ (1), Proceedings of the National Academy of Sciences USA (4), PLoS Biology (2),

    PLoS One (3), Reviews in Fish Biology and Fisheries (1), Science (1), Science Advances (1),

    Transactions of the American Fisheries Society (2).

    Books: Evolutionary Ecology of Marine Invertebrate Larvae, Oxford Press, (eds Carrier,

    Reitzel & Heyland).

    4. Reviewed Grants for the following agencies (include number of requests) National Science Foundation (8), Alaska Sea Grant (1), National Oceanic and

    Atmospheric Administration (3), National Geographic Society, Icelandic Research Fund,

    Oregon Department of Fish & Wildlife, Washington Department of Fish & Wildlife

    Contacted and participated on Grant Panels by a state or federal representative

    NSF DEB (Arlington, VA) 2016

    F. Diversity Activities

    G. Other Engagement Activities

    Outreach and Media:

    2018 Outreach publication in The Osprey, an angler-supported journal of salmon and steelhead

    conservation:

    Harder, AMG, Willoughyby JRP (2018) Great Lakes steelhead win the adaptation lottery.

    The Osprey 91: 19-21

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    2018 Additional coverage of Willoughby et al. 2018: McCallum E (2018) A fish out of salt

    water. Journal of Experimental Biology. 221:3-4.

    2015 Regular contributor to the “Molecular Ecologist”, the web log of Molecular Ecology

    Posts available at: http://www.molecularecologist.com/author/mark-christie/

    2012 Lecture and Q&A for Tri Beta Biology Honor Society, Georgia Institute of Technology

    2012 Christie et al. 2012 (PNAS) was covered by the Associated Press, NPR, The Oregonian,

    The New York Times, and other media outlets. Science daily article titled “Hatcheries

    change salmon genetics after a single generation.” It was also reviewed by Faculty of

    1000.

    2012 Carrol, Childerhouse, Christie et al. 2012 (Molecular Ecology) was covered in Science

    Daily and other news organization. Science daily article titled “First paternity study of

    southern right whales finds local fathers most successful.”

    2011 Interviewed for National Public Radio (NPR). Available at:

    http://earthfix.opb.org/water/article/taming-the-wolves-new-research-shows-hatchery-

    fish/

    2011 Lecture and Q&A session to Trout Unlimited, Eugene Oregon chapter

    2011 Outreach publication in The Osprey, an angler-supported journal of salmon and steelhead

    conservation:

    Christie M.R., McMillan J.R. (2011) Steelhead and resident rainbow relationship slowly

    revealed. The Osprey 69: 11-13.

    2011 Christie et al. 2011 (Molecular Ecology) was reviewed by K. Mobley in “News and

    Views” column of Molecular Ecology (2011) 20: 1080-1082 and featured in Audubon

    2010 Developed and implemented activities for the workshop, “Darwin’s legacy: modern

    explorations of evolutionary biology,” a program for local high school students preceding

    a lecture by Peter and Rosemary Grant. Corvallis, Oregon.

    2010 Christie et al. 2010 (PLoS ONE) was reviewed in "News" column of Nature (13 Jan

    2011) 469:146, reviewed in “Dispatches” column of Frontiers in Ecology and the

    Environment: (2010) 9(2): 91 and was also reviewed by Faculty of 1000.

    2010 Invited speaker on “Oregon Outdoors” radio show

    2006-2009 National Ocean Science Bowl: Salmon Bowl Science Judge

    2005-2007 Evolutionary biology blog co-founder/contributor

    V. Mentoring Mentoring is an essential component of my lab. Since arriving at Purdue University, I have

    mentored 7 undergraduate students in research, 4 graduate students, and 2 postdoctoral

    researchers. All of these students are currently or have conducted independent projects in my lab.

    One undergraduate student completed her honors thesis by examining the role of oxygen

    consumption in sea lamprey exposed to the lampricide TFM; these data are included in a

    manuscript that is currently in preparation. Two undergraduates are currently quantifying genetic

    diversity in Indiana Muskellunge (Esox masquinongy) and we will be presenting our findings to

    http://www.molecularecologist.com/author/mark-christie/http://earthfix.opb.org/water/article/taming-the-wolves-new-research-shows-hatchery-fish/http://earthfix.opb.org/water/article/taming-the-wolves-new-research-shows-hatchery-fish/

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    the Indiana Department of Natural Resources in the Spring. I expect that one of the two younger

    undergraduates will also pursue an honors thesis. I currently have 3 graduate students a