Umberger v. Department of Land and Natural Resources. , 140 Haw. 500 ( 2017 )


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  •     ***FOR PUBLICATION IN WEST’S HAWAIʻI REPORTS AND PACIFIC REPORTER***
    Electronically Filed
    Supreme Court
    SCWC-13-0002125
    06-SEP-2017
    08:07 AM
    IN THE SUPREME COURT OF THE STATE OF HAWAIʻI
    ---o0o---
    RENE UMBERGER, MIKE NAKACHI, KAʻIMI KAUPIKO, WILLIE KAUPIKO,
    CONSERVATION COUNCIL FOR HAWAIʻI, THE HUMANE SOCIETY OF THE
    UNITED STATES, and CENTER FOR BIOLOGICAL DIVERSITY,
    Petitioners/Plaintiffs-Appellants,
    vs.
    DEPARTMENT OF LAND AND NATURAL RESOURCES, STATE OF HAWAIʻI,
    Respondent/Defendant-Appellee.
    SCWC-13-0002125
    CERTIORARI TO THE INTERMEDIATE COURT OF APPEALS
    (CAAP-13-0002125; CIVIL NO. 12-1-2625-10 JHC)
    SEPTEMBER 6, 2017
    RECKTENWALD, C.J., NAKAYAMA, McKENNA, POLLACK, AND WILSON, JJ.
    OPINION OF THE COURT BY POLLACK, J.
    For a nominal fee per year, the Department of Land and
    Natural Resources (DLNR) authorizes the collection of fish or
    other aquatic life for aquarium purposes (aquarium collection)
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    by issuing permits pursuant to Hawaii Revised Statutes (HRS) §
    188-31 (2011) and its administrative rules.          Subject to certain
    terms and conditions contained in the permit and restrictions
    provided by statutes and administrative rules, each commercial
    aquarium collection permit authorizes the extraction of an
    unlimited number of fish or other aquatic life annually from the
    State’s coastal waters.     DLNR also issues recreational aquarium
    collection permits that authorize an annual catch limit for each
    permit of almost 2,000 fish or other aquatic life.           The
    fundamental issue presented in this case is whether aquarium
    collection pursuant to permits issued under HRS § 188-31 and
    DLNR’s administrative scheme is subject to the environmental
    review procedures provided in the Hawaii Environmental Policy
    Act (HEPA).   We hold that commercial aquarium collection under
    HRS § 188-31 and DLNR’s administrative rules is subject to
    HEPA’s requirements.     We further hold that the record is not
    adequate for this court to determine whether recreational
    aquarium collection may be exempt from HEPA.          Accordingly, we
    remand this case to the circuit court for further proceedings to
    resolve the issue of whether recreational aquarium collection
    under HRS § 188-31 and DLNR’s administrative rules is also
    subject to HEPA.
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    I. FACTS AND PROCEDURAL HISTORY
    Petitioners Rene Umberger, Mike Nakachi, Kaimi
    Kaupiko, and Willie Kaupiko identify themselves as concerned
    Hawaii citizens, avid divers, and subsistence fishermen.
    Petitioner Conservation Council for Hawaii is a nonprofit
    organization based in Hawaii with approximately 5,500 members
    worldwide whose mission is to protect native Hawaiian species
    and to restore native Hawaiian ecosystems for future
    generations.   Petitioner Humane Society of the United States, a
    national nonprofit organization with over 11 million members, is
    dedicated to the protection of wildlife and habitat.           Petitioner
    Center for Biological Diversity is a nonprofit organization
    dedicated to preserving, protecting, and restoring biodiversity,
    native species, ecosystems, and public lands; the organization
    has approximately 450,000 members, many of whom live in Hawaii.
    Respondent Department of Land and Natural Resources (DLNR) is
    the state agency that holds the statutory authority to issue
    permits for aquarium collection.
    On October 24, 2012, Petitioners filed a complaint for
    declaratory judgment and injunctive relief in the Circuit Court
    of the First Circuit (circuit court) specifically challenging
    fifty aquarium collection permits that DLNR had issued in the
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    120 days before the filing of the complaint.1           The complaint
    sought (1) a declaration that DLNR is in violation of HEPA,
    chapter 343 of the HRS, for failing to complete the HEPA review
    process prior to approving the challenged permits; (2) a
    declaration that DLNR’s issuance and renewal of these permits
    without complying with HEPA is invalid and illegal; (3) an
    injunction enjoining collection under the challenged permits
    until DLNR fully complies with HEPA; and (4) an injunction
    enjoining DLNR from approving, renewing, or issuing any aquarium
    collection permits prior to completing a HEPA review of the
    issuance of the challenged permits.2         DLNR filed an answer
    requesting a dismissal with prejudice of Petitioners’ complaint.
    Thereafter, DLNR moved for summary judgment, arguing
    that (1) DLNR’s practice of not requiring environmental review
    of applications for aquarium collection permits is entitled to
    deference and (2) environmental review is not required for
    aquarium collection permits because there is no action initiated
    by an applicant requiring agency approval (applicant action).3
    1
    In addition to these named permits, Petitioners challenged any
    other aquarium collection permits renewed or granted by DLNR in the 120 days
    prior to the filing of their complaint.
    2
    The complaint also requested that the circuit court retain
    continuing jurisdiction to review DLNR’s compliance with all judgments and
    orders.
    3
    The Honorable Jeannette H. Castagnetti presided over the
    proceedings in this case.
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    In support of DLNR’s motion for summary judgment, Alton K.
    Miyasaka, an aquatic biologist in DLNR’s Division of Aquatic
    Resources, submitted a declaration.        Miyasaka averred that
    “[a]nyone who applies for a permit pursuant to [HRS] § 188-31
    and who goes through the above process receives a permit” and
    that DLNR “does not have and does not exercise discretion with
    respect to the permits.”      Thus, according to Miyasaka, the
    process does not involve discretionary consent and there is no
    applicant action.
    Petitioners opposed DLNR’s motion for summary
    judgment, contending that (1) DLNR’s failure to comply with HEPA
    prior to issuing aquarium collection permits is not entitled to
    deference because the aquarium collection permitting statute is
    clear and not subject to agency interpretation and (2) aquarium
    collection is a HEPA “action” subject to DLNR’s discretionary
    consent.
    Petitioners cross-moved for summary judgment,
    contending that (1) HEPA mandates environmental review of
    aquarium collection permits and (2) the issuance of aquarium
    collection permits is subject to DLNR’s discretionary consent.
    In support of Petitioners’ summary judgment motion, they
    attached (1) the declarations of Gail Grabowsky, Petitioner
    Umberger, Petitioner Nakachi, Petitioner Kaimi Kaupiko,
    Petitioner Wilfred Kaupiko, Marjorie F.Y. Ziegler, Inga Gibson,
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    Miyoko Sakashita, and Dane Enos; (2) excerpts of The Report to
    the Twenty-Fifth Legislature on the Findings and Recommendations
    of Effectiveness of the West Hawaii Regional Fishery Management
    Area [hereinafter The Report to the Twenty-Fifth Legislature]4;
    (3) excerpts of Hawaii’s State of the Reef, published by DLNR’s
    Division of Aquatic Resources5; and (4) DLNR’s approval of Disney
    Aulani’s request for a special activity permit to collect
    aquarium fish for a period of one year in order to stock a
    saltwater swimming pool.
    Gail Grabowsky, an associate professor at Chaminade
    University and the Director of the University’s Environmental
    Studies Program,6 stated that commercial aquarium collectors
    4
    Petitioners relied on this report in asserting that “[o]ver 200
    species are collected for the aquarium trade in Hawaii,” that “the level of
    aquarium collection along the west coast of the island of Hawaii have
    documented substantial increases, i.e., 25 percent between 2000 and 2010, in
    the number of collectors and in the collection of certain species,” and that
    aquarium collection permits allow the collection of species that are
    “particularly vulnerable to depletion.”
    5
    Petitioners relied on this publication in explaining that DLNR is
    charged as the steward of Hawaii’s natural resources, including ocean
    ecosystems, and that DLNR manages the fourth longest coastline in the United
    States, including 410,000 acres of coral reefs. Petitioners also used this
    publication in contending that DLNR itself has previously recognized the
    detrimental effects of removal of reef fish on the coral reef ecosystem and
    that further studies in this area are necessary if this activity is to
    continue.
    6
    Grabowsky holds a bachelor’s degree and a doctorate in zoology
    from Duke University, has authored or co-authored various published
    scientific works, and has received several honors, scholarships, and grants
    in her field. As relevant here, her research has focused on ornamental reef
    fish collection on Oahu, marine invertebrate zoology, molecular/morphological
    evolution, coral reef health, sea bird habitat conservation, sea bird by-
    catch reduction, box jellyfish dispersal, and natural history in Hawaii.
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    self-report to DLNR the type and quantity of marine animals that
    they collect and that this practice results in underreporting
    because commercial collectors “may either fail to turn in catch
    reports or inaccurately quantify their catch.”           Grabowsky
    explained that “[a]quarium collectors utilize modern and ever-
    improving technologies, like scuba equipment, highly camouflaged
    wetsuits, nitrox (a mix of nitrogen and oxygen, usually with a
    higher-than-normal level of oxygen to extend dive time), GPS
    systems, and underwater scooters, to increase their ability to
    locate aquarium fish.”7
    According to Grabowsky, “although aquarium collection
    is prohibited along 35% of the west coast of the island of
    Hawaii, less than 1% of the remaining area around the Main
    Hawaiian Islands is protected.”8          Grabowsky opined that the
    drastic differences in species abundances between well-protected
    areas and those that are not “reveal[] that aquarium collection
    is removing and having detrimental effects on species that play
    important ecological roles in reef ecosystems.”           Because the
    most heavily fished species are herbivorous algae eaters,
    7
    Grabowsky declared that aquarium collectors at times also use
    underwater blankets to cover the reef so that fish would not be able to take
    refuge in the coral.
    8
    Based on other studies, Grabowsky declared that “there has been a
    severe depletion of fish” in the Main Hawaiian Islands when compared to the
    diversity and population of fish in the Northwestern Hawaiian Islands.
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    Grabowsky stated that their removal from the reef ecosystem
    decreases the reef’s ability to withstand habitat degradation
    and could result in an algal-dominated reef.           Grabowsky found
    that “the most greatly affected species are those that have been
    heavily exploited.”      Grabowsky’s survey of relevant studies
    indicated “that certain rare, vulnerable species are under
    intense collection pressure, and the effects of collection on
    many of their populations [are] unknown.”9
    Grabowsky explained that aquarium collection typically
    focuses on juvenile fish because they are smaller and more
    aesthetically pleasing and thus more popular to customers.
    According to Grabowsky, this “can result in top-heavy age
    distributions of many of the heavily collected species on reefs,
    and means that there are fewer juveniles in reef ecosystems that
    are able to grow up to reproduce as adults.”
    Based on her research and review of relevant
    scientific literature, Grabowsky concluded that “aquarium
    collection is having a detrimental effect on fish populations
    around Oahu and in other areas of the state,” it “disrupts the
    ecosystems and makes them less able to respond to other
    9
    According to Grabowsky, some of these vulnerable species, such as
    Tinker’s butterflyfish and psychedelic wrasse, have been listed on DLNR’s
    “Species of Greatest Conservation Need,” but they are still being collected
    without any limits.
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    stressors,” and “it removes animals that occupy important and
    unique ecological niches.”         Grabowsky opined that prohibiting
    collection in certain areas does not adequately address the
    problem in that, “while it may slow the disappearance of the
    fish species and reef degradation, . . . it will not prevent
    it.”    Finally, Grabowsky declared that the “data showing that
    the current permitting system and designation of protected areas
    adequately protects the reef ecosystems is lacking.”
    Petitioner Umberger also submitted a declaration
    stating that she had been diving professionally since 1983 and
    had done at least 10,000 scuba dives around the Main Hawaiian
    Islands and in various international locations.             Umberger stated
    that, based on her observations during her dives through the
    years, fish species that are highly prized by the aquarium trade
    have abruptly disappeared from a lot of dive sites.10
    Based on Umberger’s experience diving and snorkeling
    along the west coast of the island of Hawaii, she declared that
    there is a marked difference in the condition between those
    reefs that are open to collection and those that are not: reefs
    10
    For example, Umberger explained that the three dragon eels (which
    could retail for over a thousand dollars apiece) and several flame angelfish
    that she had been seeing in the Red Hill area of south Maui for years had
    disappeared. In addition, during the years that she had spent scuba diving,
    Umberger stated that she saw corals physically broken apart to expose the
    crevices in the reef.
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    open to collection have fewer colorful and aesthetically
    pleasing fish and invertebrates.         Umberger also attested that
    she had “noticed a dramatic reduction in biodiversity on reefs
    and in the density of species of fish that are collected by the
    aquarium trade.”    Finally, Umberger opined that DLNR’s current
    permitting practices “will have irreversible, negative
    consequences for Hawaii’s reef ecosystems and [her] interests in
    enjoying and protecting these precious areas.”
    Petitioner Nakachi also submitted a declaration in
    support of Petitioners’ summary judgment motion.           Nakachi stated
    that he is a resident of Kailua-Kona on the island of Hawaii and
    a scuba diving tour operator since 1987 who has gone on tens of
    thousands of scuba dives, both recreationally and as part of his
    scuba diving tour business, in and around Hawaii waters for the
    past forty years.    According to Nakachi, his “recreational and
    aesthetic interests in seeing healthy reef ecosystems full of
    colorful fish are harmed by aquarium collection under the
    challenged permits.”     Nakachi also averred that his economic
    interests are harmed because his business relies on a healthy
    marine environment in order to be successful.          Nakachi described
    his experience in which a dive site that was once populated by
    colorful fish species experienced a decline in the fish
    population and coral damage when aquarium collectors discovered
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    the dive site’s location.11       Over the years that he had spent
    diving in the waters of Hawaii, Nakachi observed “negative
    changes on the coral reefs . . . because of aquarium collection,
    particularly along the west coast of the island of Hawaii.”
    Based on Nakachi’s diving experience in State waters, he
    declared that “[t]here is a very noticeable difference in
    aquarium fish species’ populations and coral damage between the
    areas that are open to collection and the areas that are
    closed.”    Nakachi averred that his clients “have expressed
    concern . . . about the changes they see on the coral reefs
    where they dive,” the fact that there are fewer fish in the
    reefs, and damaged corals.       According to Nakachi, these concerns
    had prompted his clients not to dive in Hawaii anymore.
    Nakachi echoes Grabowsky’s description of the
    technology he had observed aquarium collectors use over the
    years, 
    see supra
    .     Based on the decline that he had witnessed in
    aquarium fish population and the health of corals where he
    dives, Nakachi stated that he is “afraid that [the] reef
    ecosystems will continue to decline until they are not able to
    sustain marine life anywhere near the previous levels.”
    11
    One site on the island of Hawaii had “no fish left” by 2006 when
    Nakachi went back to scuba dive there.
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    Petitioners Ka‘imi Kaupiko and Wilfred “Willie” Kaupiko
    also submitted declarations in support of Petitioners’ summary
    judgment motion.     The Kaupikos are Native Hawaiian subsistence
    fishermen living in the village of Miloli‘i, which is located on
    the west side of the island of Hawai‘i.         They attested that their
    cultural, subsistence, and aesthetic interests are harmed by
    DLNR’s issuance of aquarium collection permits without first
    engaging in HEPA review “because aquarium collectors remove
    species of fish that [they] fish for” and because they had
    “noticed a substantial decline in the variety and number of fish
    on reefs along the west coast of Hawai‘i over the past decade.”
    Based on the Kaupikos’ experience, when they had gone out
    fishing, they had hardly seen any types of fish that are
    collected by the aquarium trade, even in areas near Miloli‘i that
    are closed to collection.12
    Ka‘imi Kaupiko stated that the dwindling number of fish
    affects his ability to feed himself and his family and
    negatively impacts the ecosystem of which they are a part.
    Ka‘imi also declared that he had noticed coral dying after being
    damaged by boat anchors and pollution and that “removal of fish
    12
    Willie Kaupiko stated that he had seen, in January and November
    2012, aquarium collectors taking fish in areas where collection is
    prohibited.
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    for aquarium collection further disrupts an already-stressed
    ecosystem.”    Ka‘imi attested that “[t]he reefs on the west coast
    of the island of Hawai‘i do not look as healthy as they used to”
    and that he is “worried about the ability of [the] reef
    ecosystems to survive so that future generations can continue
    fishing and practicing . . . Native Hawaiian traditions.”13
    The Kaupikos concluded that aquarium collection under
    the challenged permits affects their ability to catch fish for
    food, disrupts the ecosystem, hurts the reef’s ability to
    withstand harm from things like pollution and physical damage,
    and harms their cultural, subsistence, recreational, and
    aesthetic interests, as well as their ability to use, enjoy, and
    protect the ocean and coral reefs for future generations’ use
    and education.
    Marjorie Ziegler, the Executive Director of Petitioner
    Conservation Council for Hawaii, and Miyoko Sakashita, a staff
    member of Petitioner Center for Biological Diversity (CBD),
    submitted declarations stating that the members of their
    respective organizations are harmed by DLNR’s aquarium
    collection permitting system “because it threatens to impair
    13
    Because Ka‘imi Kaupiko is involved in educating young people in
    Miloli‘i about Hawaiian cultural traditions involving fishing and the ocean,
    he also declared that aquarium collection affects his “ability to educate
    children in the village about healthy reefs and fish populations.”
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    their aesthetic, subsistence, and recreational interests in
    using, enjoying, and protecting the State’s reefs.”14            They
    further averred that “DLNR’s failure to comply with its legal
    obligations deprives” their organizations and their “members of
    both the information that would be generated through the HEPA
    process and the opportunity to participate actively in the
    process of environmental review.”
    Inga Gibson, the Hawai‘i State Director of Petitioner
    Humane Society of the United States (HSUS), declared that DLNR’s
    issuance of aquarium collection permits without HEPA review
    “adversely affects HSUS’s organizational interests in protecting
    animals from unnecessary harm, suffering, and death, as well as
    its members’ and supporters’ ability to protect, observe, and
    enjoy Hawai‘i’s coral reef animals and ecosystems that are and
    will be affected by collection under the challenged permits.”
    Gibson averred that aquarium collectors remove types of fish
    that serve a larger role in reef ecosystems, a practice that
    “has negative effects on other marine species that inhabit coral
    reefs.”    Gibson also stated that HSUS views “aquarium collection
    as a harmful, disposable trade, because up to forty percent of
    fish may die before reaching their final destination and many of
    14
    Sakashita also stated that CBD’s members, including herself,
    “regularly use Hawai‘i’s coastal waters for recreation, aesthetic enjoyment,
    observation, research, and other educational activities.”
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    the collected fish are not suitable for living in captivity,
    surviving only a fraction of their natural lives.”           Gibson
    concluded that DLNR’s permitting regime “affects HSUS’s members’
    recreational, aesthetic and educational interests in protecting,
    studying, and observing these fish and invertebrates and their
    coral reef habitats.”
    Dane Enos, a resident of Kailua-Kona and a former
    commercial aquarium fish collector, submitted a declaration in
    support of Petitioners’ summary judgment motion describing the
    procedure he followed in collecting aquarium fish before he left
    the trade.   Enos explained that his “decisions about which
    species to take and how many animals to collect were based on
    consumer demand.”    Once he received an order for a particular
    species from a wholesaler, he would “go out to the reefs to try
    and fill that order” and that “[t]he price [he] would get paid .
    . . would fluctuate depending on whether the wholesalers already
    had that particular species of fish in their shops.”           Enos’s
    practice was to “operate[] on a fourteen to eighteen month
    system of rotation at sites where [he] collected[] to give fish
    time to reproduce before going back to the same spot.”            Enos
    declared that his commercial aquarium collection permit allowed
    him “to take an unlimited type and quantity of species from
    coastal waters” and “to collect anywhere in the State of Hawai‘i
    other than in areas . . . where aquarium collection was
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    prohibited.”   Enos stated that, when he first started collecting
    in 1985, there were not as many collectors as there were when he
    left the trade in 2002.     At the tail end of his participation in
    the trade, Enos described how other collectors would take “fish
    from the same spot too frequently, affecting the number of
    animals and the balance of the ecosystem.”         Some collectors,
    according to Enos, also broke off finger corals so as to create
    a uniform surface for their nets.        Enos attested that “after
    witnessing collectors over-harvesting fish and invertebrates and
    damaging the reefs, in addition to the stress on the reefs from
    other factors, like pollution, [he] decided that [he] could not
    continue collecting” and left the trade.
    DLNR opposed Petitioners’ motion for summary judgment,
    reiterating its position that there is no HEPA “action” and no
    “approval” involved in aquarium collection and that the
    environment is not harmed by the current permitting system.                In
    support of its opposition, DLNR submitted a declaration from
    Alton Miyasaka, averring that DLNR’s Division of Aquatic
    Resources “continually monitors and studies populations of fish
    and other aquatic life potentially affected by aquarium fish
    permits issued pursuant to [HRS] § 188-31” and that the current
    population levels of aquarium fish are sustainable.           Miyasaka
    stated that the collection “areas are quite limited,” that
    Hawaii and Oahu are the “main collecting islands,” and that
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    Kauai, Molokai, and Lanai “have essentially no contribution to
    the statewide totals and may be considered unfished.”            On the
    island of Hawaii, Miyasaka continued, “35% of the 90-mile Kona
    coast is closed to aquarium collecting.”         However, Miyasaka
    stated that, although the 90-mile Kona coast “represent[s]
    approximately 12.6% of the total coastline of the state, [it]
    accounted for 68% of the statewide total catch numbers” in 2011.
    Miyasaka averred that the top ten areas where aquarium
    collection is conducted “account for 90% of all animals
    collected” and that “[t]hese top ten areas represent less than
    22% of the entire coastline.”       As such, Miyasaka represented
    that “the vast majority of the State’s coastline is largely
    unfished.”
    Miyasaka declared that the annual total for animals
    caught from 1999 to 2010 ranged from 412,587 to 1,019,720 per
    year, but he reasoned that “most of these numbers are from
    invertebrates rather than fish” (i.e., the ratio of
    invertebrates to fish ranges from 50% to close to 90% per year).
    According to Miyasaka, “this is significant because
    invertebrates generally reproduce faster than fish and therefore
    can replenish themselves faster.”        However, Miyasaka neither
    addressed nor referenced Petitioners’ contentions that were
    based on excerpts of The Report to the Twenty-Fifth Legislature
    and Hawaii’s State of the Reef, both of which were published by
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    DLNR.   See supra notes 4 & 5.      These publications stated that
    aquarium collection permits allow the collection of species that
    are particularly vulnerable to depletion and recognized the
    detrimental effects of removal of reef fish on the coral reef
    ecosystem.
    The Report to the Twenty-Fifth Legislature, on which
    Petitioners relied as part of their summary judgment motion,
    also addressed the issues surrounding the collection of
    invertebrates for aquarium purposes.        The Report stated that
    researchers studying the Florida marine aquarium fishery had
    found that “the once small ornamental fish fishery has grown
    dramatically in recent years to become a large scale
    invertebrate-dominated industry.”        The researchers noted that
    the focus of aquarium collection shifted from “purely ornamental
    species to ones providing biological services in home aquaria,”
    such as “[i]nvertebrate grazers [that] can control algal
    growth.”   The researchers concluded that “the intensive
    collecting of such species was ecologically unsound.”
    Miyasaka also described the process used in aquarium
    collection:
    Typically each animal is hand caught. The collector sets
    [the] net, guides the fish into the net, then hand scoops
    the fish off the net. Each fish is carefully selected for
    its condition (no damage to fins or body), size, and
    species. Fish that are damaged or imperfect are returned
    to the ocean. Any fish that is not the right size, color,
    or species is not taken. Little or no unwanted fish are
    taken so there is little or no bycatch (a fish that is
    taken unintentionally). This attention to detail is why
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    the marine life in the Hawaiian aquarium fishery is
    considered one of the highest quality products in the
    world.
    In their reply to DLNR’s opposition, Petitioners
    argued that aquarium collection is an “action” and that aquarium
    collection permit applications require DLNR’s “approval,” i.e.,
    discretionary consent.     In addition, Petitioners challenged
    DLNR’s assertion that aquarium collection was being conducted in
    a sustainable and environmentally sound manner, stating that
    this assertion is not based on anything other than Miyasaka’s
    conclusory declaration.     Thus, Petitioners concluded that HEPA
    applies to aquarium collection under permits issued by DLNR.
    After a hearing on the respective parties’ motions for
    summary judgment, the circuit court granted DLNR’s motion for
    summary judgment and denied Petitioners’ cross motion for
    summary judgment, reasoning that there is no applicant “action”
    that triggers HEPA in this case.         The circuit court stated that
    environmental review under HEPA is required only if there is an
    “action,” i.e., a “program” or “project.”         Because “program” and
    “project” are not statutorily defined under HEPA, the circuit
    court, relying on a generally accepted dictionary, defined
    “program” “as a ‘plan or system under which action may be taken
    toward a goal.’”    The circuit court defined “project” “as ‘a
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    15
    specific plan or design; scheme’ or a ‘planned undertaking.’”
    Because aquarium collection, according to the circuit court, is
    not a “specifically identifiable program[] or project[],” the
    court determined “that as a matter of law, ‘aquarium collection’
    is not an applicant ‘action’ that triggers HEPA.”            The circuit
    court entered its final judgment on June 24, 2013.
    II. ICA PROCEEDINGS
    Petitioners appealed from the order denying their
    cross motion for summary judgment, the order granting DLNR’s
    motion for summary judgment, and the circuit court’s final
    judgment.    In its published opinion, the Intermediate Court of
    Appeals (ICA) outlined the steps for evaluating whether an
    action is subject to environmental review.          Preliminarily, there
    must be a “program or project to be initiated by an agency or
    applicant.”    Umberger v. Dep’t of Land & Nat. Res., 138 Hawaii
    508, 512, 
    382 P.3d 320
    , 324 (App. 2016) (quoting HRS § 343–2
    (2010)).    In addition, the program or project must (1) be
    initiated by an agency or a private party and require government
    approval; (2) qualify under one or more of the nine categories
    of land uses and administrative acts enumerated in HRS § 343-
    15
    The circuit court relied on Merriam-Webster’s definition of
    “program” and “project.” See Program, Merriam-Webster, http://www.merriam-
    webster.com/dictionary/program (last visited July 13, 2017); Project,
    Merriam-Webster, http://www.merriam-webster.com/dictionary/program (last
    visited July 13, 2017).
    20
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    5(a) (2010); and (3) not be exempt under HRS § 343-6(a)(2)
    (2010).   
    Id. at 512—13,
    382 P.3d at 324—25.
    The ICA characterized the “action” in this case as
    “the ‘taking of marine or freshwater nongame fish and other
    aquatic life for aquarium purposes,’ that is initiated by an
    applicant’s request for an aquarium fish permit.”           
    Id. at 513,
    382 P.3d at 325 (quoting HRS § 188-31(a) (2011)).           The ICA
    emphasized that while the “[a]ppellants described the alleged
    action as the ‘directed, intentional, large-scale commercial
    removal under each [p]ermit, and collectively under the dozens
    of such [p]ermits DLNR issued,’” they sought “an interpretation
    of HEPA that would apply equally to both recreational and
    commercial aquarium fish permits.”        
    Id. at 513–14,
    382 P.3d at
    325–26.
    The statutory analysis of the ICA commenced with an
    examination of the meaning of “action.”         While HEPA defines
    “action” as “any program or project to be initiated by an agency
    or applicant,” the ICA acknowledged that HEPA does not define
    “program” and “project.”      
    Id. at 514,
    382 P.3d at 326 (quoting
    HRS § 343-2).   The ICA discussed various decisions issued by the
    appellate courts of Hawaii that held there was an “action” under
    HEPA such that the environmental review process was triggered.
    Those cases involved “[t]he Napilihau Villages, Mahukona Lodge,
    Koa Ridge project, harbor improvements for the Superferry
    21
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    Project, Laumaka subdivision, and a research program concerning
    genetically modified algae.”      
    Id. at 516,
    382 P.3d at 328.         In
    these cases, the ICA observed that there were “specifically
    identifiable programs or projects.”        
    Id. According to
    the ICA,
    aquarium collection is unlike any of the activities that this
    court has previously considered as programs or projects for the
    purposes of HEPA.    
    Id. In concluding
    that aquarium collection
    is not a “specifically identifiable program or project,” the ICA
    emphasized that aquarium collection “includes a parent netting
    one or two fish from a stream for his or her child’s fish tank,
    as well as larger scale commercial operations.”          
    Id. In addition,
    the ICA reasoned that HEPA review is not
    the sole mechanism through which marine life and reef ecosystem
    could be protected from unconstrained removal in large numbers.
    The ICA highlighted other statutory frameworks and
    administrative rules that allow DLNR to manage aquatic life and
    resources, including catch limits and restrictions for certain
    species applicable to commercial aquarium collection permit
    holders and DLNR’s authority to attach conditions to commercial
    marine licenses and permits.      
    Id. Further, the
    ICA noted that DLNR issues permits and
    licenses for activities similar to aquarium collection--e.g.,
    bait fish licenses, freshwater game fish licenses, hunting
    licenses, camping permits, etc.       According to the ICA, there is
    22
    ***FOR PUBLICATION IN WEST’S HAWAIʻI REPORTS AND PACIFIC REPORTER***
    “no rational distinction or logical reason why HEPA
    environmental review procedures should be required for aquarium
    fish permits, but not for these other types of licenses and
    permits.”   
    Id. Thus, the
    ICA concluded that aquarium collection
    under permits issued pursuant to HRS § 188-31 does not qualify
    as a HEPA “action.”       
    Id. at 517,
    382 P.3d at 329.
    The ICA, however, rejected DLNR’s argument “that, even
    if aquarium collection fell within the definition of an
    ‘applicant action,’ it is not subject to HEPA because there is
    no discretionary agency approval of aquarium fish permits.”                
    Id. at 517–18,
    382 P.3d at 329–30.       The ICA determined that the fact
    that the application for an aquarium fish permit is online and
    completely automatic does not equate to DLNR lacking discretion
    because the plain language of HRS § 188-31, as supported by its
    legislative history, explicitly confers discretion on DLNR in
    deciding whether to approve an application.          
    Id. at 518,
    382
    P.3d at 330.   The ICA also reasoned that the online application
    “is simply the means by which DLNR has determined to exercise
    its discretion.”    
    Id. Thus, the
    ICA affirmed the circuit
    court’s judgment that granted DLNR’s motion for summary judgment
    and denied Petitioners’ cross motion for summary judgment.             
    Id. III. ARGUMENTS
    ON CERTIORARI
    In their application for writ of certiorari,
    Petitioners advance four contentions: (1) the legislature
    23
    ***FOR PUBLICATION IN WEST’S HAWAIʻI REPORTS AND PACIFIC REPORTER***
    intended the words “program” and “project” to encompass a broad
    scope of human activity, including aquarium collection; (2) HEPA
    applies to individuals and provides mechanisms to resolve
    practical difficulties that may be encountered during the
    environmental review process16; (3) the ICA’s construction of
    “program or project” undermines DLNR’s public trust and
    statutory duties to conserve Hawaii’s marine resources; and (4)
    other regulatory tools that DLNR possesses are not substitutes
    for HEPA, nor do such tools excuse violations of HEPA.
    In its response, DLNR contends that (1) the ICA was
    correct in concluding that aquarium collection is not an
    “action” within the meaning of HEPA; (2) the environment is not
    harmed by the present system and any harm to the environment is
    irrelevant to the analysis; (3) Petitioners’ argument regarding
    public trust was never pleaded and, in any event, does not
    assist this court in construing HRS chapter 343; and (4) the ICA
    erred in holding that the issuance of aquarium collection
    permits requires DLNR’s discretionary consent.
    16
    Petitioners argue that the ICA’s concern about one-fish
    recreational aquarium collection is unjustified because that activity may be
    exempted from HEPA pursuant to HRS § 343-6(a)(2) (2010) as it may fall within
    one of DLNR’s exempt categories--minor alteration in the conditions of land,
    water, or vegetation. Petitioners also assert that “tiering,” which allows
    an agency to incorporate previous environmental assessments and impact
    statements or to group similar actions in a single environmental assessment
    or impact statement, would address the ICA’s apparent concern about the
    burden on small-time aquarium collectors of complying with HEPA’s
    requirements.
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    IV. STANDARDS OF REVIEW
    A trial court’s ruling on a motion for summary
    judgment is reviewed de novo under the right/wrong standard.
    Salera v. Caldwell, 137 Hawaii 409, 415, 
    375 P.3d 188
    , 194
    (2016).   “The interpretation of a statute is a question of law
    reviewable de novo.”     Kauai Springs, Inc. v. Planning Comm’n of
    Cty. of Kauai, 133 Hawaii 141, 163, 
    324 P.3d 951
    , 973 (2014)
    (quoting Franks v. City & Cty. of Honolulu, 
    74 Haw. 328
    , 334,
    
    843 P.2d 668
    , 671 (1993)).
    V. DISCUSSION
    The central question in this case is whether aquarium
    collection pursuant to permits issued under HRS § 188-31 (2011)
    and DLNR’s administrative rules is subject to the environmental
    review provisions of HEPA.      An environmental assessment under
    HEPA is required if three conditions are satisfied: (1) the
    proposed activity is an “action” under HRS § 343-2 (2010); (2)
    the action proposes one or more of the nine categories of land
    uses or administrative acts enumerated in HRS § 343-5(a) (2010);
    and (3) the action is not declared exempt pursuant to HRS § 343-
    6(a)(2) (2010).    See Sierra Club v. Dep’t of Transp. of the
    State of Haw., 115 Hawaii 299, 306, 
    167 P.3d 292
    , 299 (2007).
    In cases where the proposed action is initiated by a private
    party for approval by a government agency, an additional
    25
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    requirement is that the agency exercises discretionary consent
    in the approval process.      HRS § 343-5(e) (Supp. 2012).        The
    circuit court granted DLNR’s summary judgment motion and denied
    Petitioners’ cross motion for summary judgment on the grounds
    that aquarium collection under HRS § 188-31 is not a HEPA
    “action.”    Thus, if there is a genuine issue of material fact as
    to whether aquarium collection is a HEPA “action,” then summary
    judgment in favor of DLNR on this basis was erroneous.            If, on
    the other hand, there is no genuine issue of material fact that
    aquarium collection under HRS § 188-31 and the DLNR
    administrative scheme is a HEPA “action,” that it falls within
    one of the categories of land uses or administrative actions set
    forth in HRS § 343-5(a), that it is not exempt from HEPA, and
    that the issuance of a permit requires DLNR’s exercise of
    discretionary consent, then the circuit court erred in denying
    Petitioners’ cross motion for summary judgment.
    A. Whether Issuance of a Permit for Aquarium Collection is a
    HEPA “Action”
    1. The Plain-Language Construction of “Action” under HRS § 343-2
    To determine whether aquarium collection is a HEPA
    “action,” we begin by interpreting HRS § 343-2, which sets forth
    the statutory definition of “action.”        HEPA defines “action” as
    “any program or project to be initiated by any agency or
    26
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    applicant.”17    HRS § 343-2.     “Program” and “project” are not
    defined terms under HEPA.       As such, “this court may resort to
    legal or other well accepted dictionaries as one way to
    determine the ordinary meaning” of those words.           State v.
    Guyton, 135 Hawaii 372, 378, 
    351 P.3d 1138
    , 1144 (2015) (quoting
    State v. Pali, 129 Hawaii 363, 370, 
    300 P.3d 1022
    , 1029 (2013)).
    “Program” is generally defined as “a plan or system under which
    action may be taken toward a goal.”18         “Project” is defined as “a
    specific plan or design” or “a planned undertaking.”19
    In determining whether aquarium collection is a
    program or project, the crucial first step is properly defining
    the activity authorized by aquarium collection permits issued by
    DLNR.     See Sierra Club, 115 Hawaii at 306 
    n.6, 167 P.3d at 299
    n.6 (“An important preliminary step in assessing whether an
    ‘action’ is subject to environmental review is defining the
    action itself.”).     HRS § 188-31(a) provides that
    17
    It follows from this definition that there are two types of HEPA
    “actions”: agency actions and applicant actions. Sierra Club, 115 Hawaii at
    
    306, 167 P.3d at 299
    . The parties’ position in this case is that aquarium
    collection under HRS § 188-31 constitutes an applicant action and not an
    agency action. An applicant action is initiated “by a private party who
    requires government approvals for the project to proceed.” 
    Id. 18 Program,
    Merriam-Webster, https://www.merriam-
    webster.com/dictionary/program (last visited July 14, 2017).
    19
    Project, Merriam-Webster, https://www.merriam-
    webster.com/dictionary/project (last visited July 14, 2017).
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    [e]xcept as prohibited by law, the department, upon receipt
    of a written application, may issue an aquarium fish
    permit, not longer than one year in duration, to use fine
    meshed traps, or fine meshed nets other than throw nets,
    for the taking of marine or freshwater nongame fish and
    other aquatic life for aquarium purposes.[20]
    This statutory subsection, together with DLNR’s administrative
    rules, allows permit applicants to engage in two general types
    of activities: recreational aquarium collection and commercial
    aquarium collection.
    Recreational aquarium collection permits--those
    “issued . . . for non-commercial use,” Hawaii Administrative
    Rules (HAR) § 13-77-2 (effective 2015)--allow the extraction of
    up to “five fish or aquatic life specimens per person per day,”
    HAR § 13-75-14 (effective 2007).          Thus, each recreational permit
    authorizes the collection of up to 1,825 fish or other aquatic
    life within a one-year period.        
    Id. In the
    case of commercial
    aquarium collection permits, which is intended for issuance to
    persons who collect “for profit or gain or as a means of
    livelihood,” HAR § 13-74-1 (effective 2010), DLNR has not
    promulgated any rules that establish limits on the total number
    of fish and other aquatic life that commercial collectors may
    extract for the entire period in which the permits are
    20
    Although permits issued under HRS § 188-31 are valid for no
    longer than one year, DLNR allows such permits to be renewed instead of
    requiring holders of expired permits to reapply. See Licenses & Permits,
    State of Haw. Division of Aquatic Resources,
    http://dlnr.hawaii.gov/dar/licenses-permits/ (last visited July 24, 2017).
    28
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    effective.    See HAR § 13-75-14 (providing a total catch limit
    only for recreational collection).21
    HRS § 188-31 also clearly delineates the aquarium
    collection practices that must be complied with to obtain a
    permit when aquarium collectors are allowed to use fine meshed
    traps or nets to take fish and other aquatic life for aquarium
    purposes.    Subsection (b) of HRS § 188-31 states that, “[e]xcept
    as prohibited by law, the permits shall be issued only to
    persons who can satisfy the department that they possess
    facilities to and can maintain fish and other aquatic life alive
    and in reasonable health.”       HRS § 188-31(b).
    The extraction of fish or other aquatic life under
    aquarium collection permits is also limited to “aquarium
    purposes,” HRS § 188-31(c), which, per the statute, “means to
    hold salt water fish, freshwater nongame fish, or other aquatic
    life alive in a state of captivity as pets, for scientific
    21
    A few statutes and regulations restrict or limit the manner and
    extent to which aquarium collection may be conducted: bag and size limits for
    certain aquatic species on Oahu (see HAR § 13-77-6(b), (c), (d) (effective
    2015)) and in West Hawaii (see HAR § 13-60.4-4 (effective 2013)), length and
    height requirements for allowed mesh nets that apply to Oahu (see HAR § 13-
    77-6(a)), monthly reporting requirements for commercial collectors (see HRS
    §§ 189-3 (2011), 189-3.5 (2011); HAR § 13-74-20(d) (effective 2010)), and
    DLNR’s power pursuant to HAR § 13-75-14(4) (effective 2007) to attach
    conditions to commercial permits. Permits issued are also subject to terms
    and conditions imposed by DLNR that are generally consistent with or
    reference the statutes and rules that relate to aquarium collection.
    29
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    study, or for public exhibition or display, or for sale for
    these purposes,” HRS § 188-31(d)(1).
    Based on the language of HRS § 188-31, the framework
    it establishes, and the administrative rules that DLNR
    promulgated pursuant to HRS § 188-31, the defined activity
    authorized under an aquarium collection permit is as follows:
    (1)   the extraction annually from State waters of
    an unlimited number of fish or other aquatic
    life for profit or other gains (in the case
    of commercial aquarium collection) or of
    1,825 fish or other aquatic life for non-
    commercial purposes (in the case of
    recreational aquarium collection), subject
    to the terms and conditions of the permit
    and restrictions set by law;
    (2)   through the use of fine meshed nets or
    traps;
    (3)   by individuals who can satisfy DLNR that
    they possess facilities that can maintain
    aquatic life alive and in reasonable health;
    and
    (4)   for the purpose of holding aquatic life
    alive in a state of captivity as pets, for
    scientific study, or for public exhibition
    or display, or for sale for these purposes.
    The course and scope of conduct allowed by both
    recreational and commercial aquarium collection permits issued
    under HRS § 188-31 and DLNR’s administrative scheme encompass
    30
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    activity that qualifies as a “program” or “project.”           The
    activity is a “specific plan” or “a planned undertaking”--and,
    therefore, a “project”--because it involves the systematic and
    deliberate extraction of aquatic life using procedures,
    equipment, facilities, and techniques authorized or required by
    HRS § 188-31 and related administrative rules for the specific
    purpose of holding captive such aquatic life for aquarium
    purposes in order to earn profit (in the case of commercial
    permit holders) or for non-commercial use (in the case of
    recreational permit holders).
    In the same vein, both recreational and commercial
    aquarium collection are “programs” within the plain meaning of
    that word: the “plan or system under which action may be taken”
    is the purposeful and methodical extraction of aquatic life from
    State waters through the use of fine meshed nets and traps and
    the transfer of such aquatic life to facilities that are capable
    of keeping the collected aquatic life alive.          The “desired goal”
    is to take aquatic life from its habitat and hold it in a state
    of captivity for aquarium purposes, as defined by HRS § 188-
    31(d)(1), in order to earn profits (in the case of commercial
    permit holders) or for non-commercial use (in the case of
    recreational permit holders).       Additionally, the method by which
    extraction is accomplished involves instruments and techniques
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    that enhance the efficiency and amount of the collection.22
    Accordingly, aquarium collection conducted under permits issued
    pursuant to HRS § 188-31 and DLNR’s administrative rules is a
    “program or project” and therefore constitutes a HEPA “action.”
    2. HEPA’s Purpose and Structure Support the Plain-Language
    Construction of the Word “Action”
    Our interpretation of “action,” together with our
    conclusion that aquarium collection under HRS § 188-31 and
    DLNR’s administrative rules constitutes a HEPA “action,” is
    confirmed by the purpose of HEPA, as explained in HRS § 343-1
    (2010), and by HEPA’s framework.          See State v. Bovee, 139 Hawaii
    530, 544 n.13, 
    394 P.3d 760
    , 774 n.13 (2017) (explaining that
    laws in pari materia--those dealing with the same subject
    matter--shall be construed with reference to each other); State
    v. Alangcas, 134 Hawaii 515, 526, 
    345 P.3d 181
    , 192 (2015)
    (stating that legislative history is relevant in statutory
    construction even when the language appears clear because it
    ensures that the literal interpretation is consonant with the
    22
    The declarations that Petitioners submitted, describing several
    aquarium collection practices that holders of permits employ, firmly support
    the conclusion that aquarium collection under HRS § 188-31 is both a
    “program” and “project”: sophisticated and advanced techniques--such as the
    use of scuba technology, underwater jet propulsion systems, nitrox tanks,
    fizzing, underwater blankets, etc.--are utilized to extract aquatic life from
    State waters for aquarium purposes. These averments illustrate how
    elaborate, methodical, and systematic aquarium collection under HRS § 188-31
    is practiced in order to achieve the ultimate purpose of holding captive
    aquatic life for specific, statutorily enumerated purposes.
    32
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    underlying policy that the legislature sought to implement
    through the statute, thereby avoiding an absurd or unjust
    result).
    It has been frequently stated that “HEPA’s purpose is
    ‘to establish a system of environmental review which will ensure
    that environmental concerns are given appropriate consideration
    in decision making along with economic and technical
    considerations.’”    Nuuanu Valley Ass’n v. City & Cty. of
    Honolulu, 119 Hawaii 90, 103, 
    194 P.3d 531
    , 544 (2008) (quoting
    HRS § 343–1).   The Hawaii Legislature enacted HEPA after finding
    “that an environmental review process will integrate the review
    of environmental concerns with existing planning processes of
    the State and counties and alert decision makers to significant
    environmental effects which may result from the implementation
    of certain actions.”     HRS § 343-1.     The legislature also found
    “that the process of reviewing environmental effects is
    desirable because environmental consciousness is enhanced,
    cooperation and coordination are encouraged, and public
    participation during the review process benefits all parties
    involved and society as a whole.”        
    Id. Environmental impact
    statements also “allow decision-makers to make informed
    decisions” when confronted by certain proposed actions.            H.
    Stand. Comm. Rep. No. 521, in 2005 House Journal, at 1242.
    33
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    The purpose of HEPA and the legislature’s intent in
    enacting HEPA indicate that it was not meant to be applied only
    to a narrow set of activities.        See generally Pearl Ridge
    Estates Cmty. Assʻn v. Lear Siegler, Inc., 
    65 Haw. 133
    , 140–41,
    
    648 P.2d 702
    , 707 (1982) (noting that HEPA’s scope is wider
    “than the federal or the typical state analogue” (quoting
    Molokai Homesteaders Coop. Ass’n v. Cobb, 
    63 Haw. 453
    , 465, 
    629 P.2d 1134
    , 1143 (1981))).       This determination is supported by
    the wide range of activities and courses of conduct to which
    HEPA has been applied, including construction of buildings,
    expansion of or modifications to preexisting buildings,
    development of residential communities, and other real estate
    developments;23 construction on government lands in order to
    build or connect to sewage lines, waterlines, or other
    infrastructure;24 development of public transportation;25
    23
    See Unite Here! Local 5 v. City & Cty. of Honolulu, 123 Hawaii
    150, 155, 
    231 P.3d 423
    , 428 (2010) (expansion of the Turtle Bay resort,
    including the addition of hotel and condominium units and infrastructure);
    Nuuanu Valley Ass’n, 119 Hawaii at 
    94, 194 P.3d at 535
    (development of a
    subdivision consisting of nine residential lots); Price v. Obayashi Haw.
    Corp., 81 Hawaii 171, 173, 
    914 P.2d 1364
    , 1366 (1996) (recreational
    development project on the North Shore of Oahu); Kahana Sunset Owners Ass’n
    v. Cty. of Maui, 86 Hawaii 66, 68, 
    947 P.2d 378
    , 380 (1997) (multi-family
    residential development on Maui); Waikiki Resort Hotel, Inc. v. City & Cty.
    of Honolulu, 
    63 Haw. 222
    , 224, 
    624 P.2d 1353
    , 1356–57 (1981) (construction of
    a hotel building in Waikīkī); Hewitt v. Waikiki Shopping Plaza, 
    6 Haw. App. 387
    , 390, 
    722 P.2d 1055
    , 1057 (1986) (construction of a shopping and parking
    complex in Waikīkī).
    24
    See Sierra Club v. Office of Planning, State of Haw., 109 Hawaii
    411, 413, 
    126 P.3d 1098
    , 1100 (2006) (tunneling underneath several state
    highways in order to construct a sewage transmission line and a water
    (continued . . .)
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    construction of power generating facilities and the drilling of
    exploratory geothermal wells;26 the growing of imported algae on
    facilities in state lands;27 and the Management Plan of the
    Observatory Site on the summit of Haleakala
    ̅ in which a new solar
    telescope was under construction.28         The commonality among the
    varied activities to which HEPA has been applied is their
    potential of producing “environmental concerns” that HEPA
    intended to be “given appropriate consideration in decision
    making along with economic and technical considerations.”               See
    Nuuanu Valley Ass’n, 119 Hawaii at 
    103, 194 P.3d at 544
    (quoting
    (continued . . .)
    transmission line); Citizens for Prot. of N. Kohala Coastline v. Cty. of
    Haw., 91 Hawaii 94, 103, 
    979 P.2d 1120
    , 1129 (1999) (construction of
    underpasses below a state highway for golf carts); McGlone v. Inaba, 
    64 Haw. 27
    , 29, 
    636 P.2d 158
    , 160–61 (1981) (construction of underground utilities on
    state conservation land); Molokai Homesteaders Coop. 
    Ass’n, 63 Haw. at 455
    ,
    629 P.2d at 1137 (use of transmission facilities of the Molokai Irrigation
    System to transport water to a resort complex on the west end of Molokai);
    Life of the Land v. Ariyoshi, 
    59 Haw. 156
    , 157–67, 
    577 P.2d 1116
    , 1117 (1978)
    (construction of the Central Maui Water Transmission System).
    25
    See Sierra Club, 115 Hawaii at 
    305, 167 P.3d at 298
    (proposed
    developments to the Kahului Harbor in order to accommodate the operations of
    the Hawaii Superferry project).
    26
    Kepoo v. Kane, 106 Hawaii 270, 275, 
    103 P.3d 939
    , 944 (2005)
    (power generating facility); Medeiros v. Haw. Cty. Planning Comm’n, 8 Haw.
    App. 183, 186, 
    797 P.2d 59
    , 61 (1990) (drilling of four exploratory
    geothermal wells); Waianae Coast Neighborhood Bd. v. Hawaiian Elec. Co., 
    64 Haw. 126
    , 127, 
    637 P.2d 776
    , 777 (1981) (addition of an electric generating
    plant on Oahu).
    27
    Ohana Pale Ke Ao v. Bd. of Agric., State of Haw., 118 Hawaii 247,
    254, 
    188 P.3d 761
    , 768 (App. 2008).
    28
    Kilakila O Haleakala v. Univ. of Hawaii, 138 Hawaii 364, 371,
    
    382 P.3d 176
    , 183 (2016).
    35
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    HRS § 343-1).       The diversity of the subject matter of previous
    HEPA cases affirms that the word “action” has not been (and
    should not be) narrowly construed.            In this light, our
    determination that aquarium collection is a HEPA “action”
    furthers HEPA’s purpose as stated under HRS § 188-31: it “will
    ensure that environmental concerns are given appropriate
    consideration in decision making” so as to foster a holistic and
    thoughtful decisional process.           HRS § 343–1.     Given the nature,
    magnitude, and scale of aquarium collection under HRS § 188-31
    and DLNR’s administrative rules, any environmental effects that
    aquarium collection may have fall squarely within the ambit of
    what HEPA’s environmental review framework intends to integrate
    into governmental decision making.29
    Lastly, our interpretation of “action” and our
    conclusion that it includes aquarium collection pursuant to
    permits issued under HRS § 188-31 and DLNR’s administrative
    rules are also supported by HEPA’s framework.              As discussed, the
    fact that a proposed activity qualifies as an “action” does not
    mean that it would require environmental review, since the
    activity must also fall within a statutory category listed in
    HRS § 343-5(a) and not be exempt from HEPA.              See Sierra Club,
    29
    Compare the challenged activities in previous HEPA cases, supra
    notes 23—28.
    36
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    115 Hawaii at 
    306, 167 P.3d at 299
    .        And for applicant actions,
    as in this case, the agency must exercise discretionary consent
    as to the proposed activity in order for the activity to be
    subject to HEPA.    See infra Part V.D.      Thus, our interpretation
    of “action,” which would include a range of activities that has
    the potential of producing environmental effects, is supported
    by the HEPA framework because other steps in the HEPA analysis
    serve to counterbalance the scope of the meaning of “action.”
    That is, the succeeding steps in the HEPA analysis filter
    activities that qualify as “actions” in order to determine which
    “actions” actually require environmental review.
    3. The ICA Erred in its Analysis
    The ICA, in the course of conducting a plain-language
    interpretation of HEPA “action,” noted that the circuit court
    used a well-accepted dictionary to define “program” and
    “project.”   Umberger v. Dep’t of Land & Nat. Res., 138 Hawaii
    508, 514, 
    382 P.3d 320
    , 326 (App. 2016).         The ICA concluded that
    aquarium collection under HRS § 188-31 is not a HEPA “action”
    because (1) none of the other cases decided by Hawaii appellate
    courts involved activity similar to aquarium collection; (2) a
    permit might include a situation in which a parent collects one
    or two fish or other aquatic life for use in a home aquarium;
    (3) other statutes and administrative rules exist that
    37
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    sufficiently regulate aquarium collection; and (4) other
    permitting regimes would be subject to HEPA environmental review
    if aquarium collection under HRS § 188-31 were considered an
    “action.”    
    Id. at 515—17,
    382 P.3d at 327—29.
    With respect to the ICA’s first line of reasoning, it
    concluded that aquarium collection is not a HEPA “action”
    because, compared to any of the activities involved in previous
    HEPA cases, it is not a “specifically identifiable program or
    project.”    
    Id. at 516,
    382 P.3d at 328.        However, as discussed,
    the class of activities and courses of action that HEPA covers
    is broad so as to successfully effectuate the intent and purpose
    of the statutory scheme.       See supra notes 23—28.       Additionally,
    there has been no HEPA case in which this court determined
    whether an activity is a HEPA “action” by evaluating its
    similarity to the challenged activities in other HEPA cases.
    Doing so would unreasonably delimit HEPA’s application in a
    manner inconsistent with its purpose.30
    The ICA’s second line of reasoning is that it would be
    “unprecedented” to apply HEPA to the hypothetical situation in
    30
    Further, if the similarity of aquarium collection to a previous
    activity to which HEPA was applied is a relevant consideration on whether
    aquarium collection is an “action,” then aquarium collection qualifies as an
    “action” because it is similar to Disney Aulani’s request for a permit to use
    small mesh nets to collect live marine life for stocking a saltwater swimming
    pool. Under the ICA’s analysis, just as Disney Aulani’s proposed activity
    was deemed to be a HEPA “action,” so would aquarium collection under permits
    issued pursuant to HRS § 188-31 and DLNR’s administrative rules.
    38
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    which a “parent net[s] one or two fish from a stream for his or
    her child’s fish tank.”     Umberger, 138 Hawaii at 
    516, 382 P.3d at 328
    .   The premise of this line of reasoning is that, even
    though recreational aquarium collection permits authorize the
    extraction of almost 2,000 fish or other aquatic life per person
    annually, for the purpose of determining whether HEPA applies,
    the focus should be on the possibility that a person would use
    his or her recreational aquarium collection permit to take only
    one or two fish.
    This analysis is flawed because the properly defined
    activity for the purposes of the HEPA analysis must encompass
    the outer limits of what the permits allow and not only the most
    restrictive hypothetical manner in which the permits may be
    used.   That is, as discussed, the analysis must proceed from the
    properly defined activity allowed under aquarium collection
    permits, 
    see supra
    Part V.A. (defining the activity authorized
    under HRS § 188-31 and DLNR’s related administrative rules).
    See Sierra Club, 115 Hawaii at 306 
    n.6, 167 P.3d at 299
    n.6.
    In addition, a parent netting one or two fish for a
    home aquarium may not even be within the ambit of HRS § 188-31
    because aquarium collection permits are required only if the
    applicant intends “to use fine meshed traps, or fine meshed nets
    other than throw nets, for the taking of marine or freshwater
    nongame fish and other aquatic life for aquarium purposes.”                HRS
    39
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    § 188-31(a).     DLNR expounds on this distinction on its own
    website, informing the public that a permit to collect fish and
    other aquatic life for a home aquarium is not required “if a)
    the net has large mesh (more than two inches mesh); b) the net
    has small mesh but is less than three feet in length, height, or
    width, including the handle; or c) using a slurp gun.”              FAQ’s,
    State of Haw. Division of Aquatic Resources,
    http://dlnr.hawaii.gov/dar/fishing/faqs/ (last visited July 11,
    2017).     Under these circumstances, the act of netting one or two
    fish would not constitute aquarium collection under HRS § 188-31
    and, consequently, would not be a HEPA “action.”31            Lastly, the
    situation postulated by the ICA--a parent netting one or two
    fish or other aquatic life for recreational purposes--is not
    present in this case,32 and DLNR’s own evidence in fact showed
    that, from 1999 to 2010, millions of aquatic life were harvested
    under aquarium collection permits issued pursuant to HRS § 188-
    31.
    31
    In addition, a parent collecting one or two fish for recreational
    purposes would not fall within any of the categories of land uses and
    administrative acts under HRS § 343-5(a), see infra Part V.B. & note 47, and
    even if it were to qualify under any of the categories under HRS § 343-5(a),
    a parent engaging in aquarium collection of this nature may also be exempt
    from HEPA, see infra Part V.C. & note 51.
    32
    Petitioners also emphasize in their application for writ of
    certiorari that this scenario is not part of the record in this case.
    40
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    In holding that aquarium collection does not
    constitute a HEPA “action,” the ICA also reasoned that there is
    a “panoply of other regulatory tools that are in place” “to
    protect marine life and the reef ecosystem from the
    ‘unconstrained removal’ of large numbers of aquarium fish.”
    Umberger, 138 Hawaii at 
    516, 382 P.3d at 329
    .           The regulations
    that the ICA identified include bag and size limits for certain
    aquatic species on Oahu (see HAR § 13-77-6(b), (c), (d)
    (effective 2015)), length and height requirements for allowed
    mesh nets that apply to Oahu (see HAR § 13-77-6(a)), monthly
    reporting requirements for commercial collectors (see HRS §§
    189-3 (2011), 189-3.5 (2011); HAR § 13-74-20(d) (effective
    2010)), and DLNR’s power pursuant to HAR § 13-75-14(4)
    (effective 2007) to attach other conditions to commercial
    permits.   Umberger, 138 Hawaii at 
    516–17, 382 P.3d at 328
    –29.33
    However, as the ICA itself acknowledged, these regulations and
    statutory frameworks are not “dispositive” of whether aquarium
    collection pursuant to HRS § 188-31 and DLNR’s administrative
    rules is a HEPA action.      
    Id. at 517,
    382 P.3d at 329.         Further,
    33
    The ICA also referenced statutory provisions governing Marine
    Life Conservation Districts, Regional Fisheries Management Areas (including
    Fish Replenishment Areas), Shoreline Fisheries Management Areas (including
    Marine Protection Areas), and Marine Refuges. Umberger, 138 Hawaii at 516–
    
    17, 382 P.3d at 328
    –29.
    41
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    none of these regulations and statutes defines or modifies
    aquarium collection pursuant to HRS § 188-31 and DLNR’s
    administrative rules in a manner that would exclude such
    collection from the meaning of “action” under HEPA.34
    The ICA’s reasoning that other statutes and rules that
    overlap with HEPA could somehow place certain activities outside
    of the meaning of “action” or preclude the application of HEPA
    to such activities is also contradicted by its own precedent.
    As the ICA itself recognized in Ohana Pale Ke Ao, where HEPA
    overlaps and is consistent with another chapter of the HRS, both
    would be given effect.      Ohana Pale Ke Ao v. Bd. of Agric., State
    of Haw., 118 Hawaii 247, 255, 
    188 P.3d 761
    , 769 (App. 2008).
    Here, there is no hindrance to giving effect to the statutes and
    34
    The ICA’s suggestion that the number or comprehensiveness of
    agency rules plays a significant role in determining whether an activity
    qualifies as a HEPA “action” generates numerous evaluative considerations and
    other complications. For example, there is no standard for deciding whether
    a statutory or regulatory scheme is sufficiently comprehensive, protective,
    and enforced as to render a regulated activity not a HEPA “action.” In
    addition, the existence of other statutes and rules concerning a particular
    activity does not necessarily mean that their purpose would be identical to
    that of HEPA or that they, in fact, are sufficiently protective. In this
    case, for example, despite the statutes and rules that the ICA underscored in
    its opinion, excerpts of publications that Petitioners submitted in support
    of their motion for summary judgment illustrate the detrimental effects of
    aquarium collection to fish population and coral reef ecosystems.
    Further, the feasibility of the ICA’s analysis is also predicated
    on the assumption that any comprehensive statutory or regulatory scheme in
    place is strictly enforced. However, there is no evidence in the record that
    could support this assumption. Petitioner Willie Kaupiko declared that some
    aquarium collectors fish in prohibited areas, that he reported the incidents
    to DLNR, that DLNR is non-responsive or slow to respond, and that DLNR did
    not investigate the allegations.
    42
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    regulations identified by the ICA while also applying the
    requirements of HEPA to aquarium collection because the statutes
    and regulations have not been demonstrated to be inconsistent
    with HEPA.    See id.35
    Further, as mentioned, HEPA’s purpose is “to establish
    a system of environmental review which will ensure that
    environmental concerns are given appropriate consideration in
    decision making along with economic and technical
    considerations.”     HRS § 343–1.     If the fact that other laws and
    rules that facially appear to bear upon the environmental
    effects of an activity would exclude the activity from HEPA’s
    purview, then this would frustrate HEPA’s purpose of requiring
    agencies to appropriately consider environmental concerns in
    their decision-making process.        In other words, under the ICA’s
    analysis, an agency would be able to bypass the protections
    provided through HEPA by promulgating administrative rules that
    appear to address or bear upon the possible environmental
    effects of an activity that the agency regulates without
    actually engaging in the informed and deliberate decision-
    making process that HEPA requires.
    35
    No evidence was presented to demonstrate any inconsistency
    between HEPA, on the one hand, and the statutes and rules that the ICA
    referenced in its opinion, on the other. DLNR does not argue (nor has it
    argued in the lower courts) that such an inconsistency exists.
    43
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    The ICA’s final reason for its holding that aquarium
    collection under HRS § 188-31 is not a HEPA “action” is that
    Petitioners “offered no rational distinction or logical reason
    why HEPA environmental review procedures should be required for
    aquarium fish permits, but not for . . . other types of licenses
    and permits,” including (among others) bait fish licenses,
    commercial marine licenses, special activity permits, permits to
    enter or conduct activities in certain areas, hunting licenses,
    camping permits, collecting permits, and commercial activity
    permits.   Umberger, 138 Hawaii at 
    517, 382 P.3d at 329
    .
    Implicit in the ICA’s reasoning is the concern that, if aquarium
    collection under HRS § 188-31 were considered a HEPA “action”
    subject to environmental review, other permitting regimes
    administered by government agencies would also be subject to
    environmental review.     See 
    id. However, the
    fact that aquarium
    collection is conducted pursuant to the permitting scheme that
    DLNR administers does not drive the conclusion that aquarium
    collection is a HEPA “action” or that HEPA applies.           The
    activities authorized by the permitting schemes that the ICA
    utilized in its analysis are not effective points of comparison
    given their substantial differences, both in magnitude and
    nature, from the activities sanctioned by aquarium collection
    permits.   For example, many of the activities under the
    44
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    permitting regimes that the ICA identified do not appear to be
    “programs” or “projects.”
    Further, as stated, in order for HEPA to apply, the
    activity must be an action that falls within a category
    enumerated in HRS § 343-5(a), discussed infra Part V.B., and not
    be exempt, discussed infra Part V.C.           See Sierra Club, 115
    Hawaii at 
    306, 167 P.3d at 299
    .          And for applicant actions, an
    additional prerequisite is that the action must be subject to an
    agency’s exercise of discretionary consent, discussed infra Part
    V.D.    Thus, concluding that aquarium collection under HRS § 188-
    31 and DLNR’s administrative rules is a HEPA “action” or is
    subject to HEPA does not necessarily prescribe a determination
    that activities under other permitting regimes are also HEPA
    “actions” or are subject to HEPA’s environmental review
    requirements.      Such activities must independently meet the
    analytical framework set forth in Sierra Club and discussed in
    this case.
    Based on the foregoing, the ICA’s analysis did not
    proceed from a full and proper definition of the activity
    authorized under aquarium collection permits.             Instead, the ICA
    appeared to focus on an extreme hypothetical subset of the
    activity being proposed.         In addition, the ICA improperly relied
    on other statutes, administrative rules, and other permitting
    45
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    regimes in its analysis.       For these reasons, the ICA erred in
    concluding that aquarium collection is not a HEPA “action.”36
    B. Whether Aquarium Collection Falls Within One or More of the
    Nine Categories Listed Under HRS § 343–5(a)
    For an activity to be subject to HEPA environmental
    review, the second requirement is that it must fall within at
    least one category of land uses or administrative acts (known as
    “triggers”) enumerated in HRS § 343-5(a) (2010).37           See Sierra
    Club v. Dep’t of Transp. of the State of Haw., 115 Hawaii 299,
    306, 
    167 P.3d 292
    , 299 (2007).        DLNR conceded for the purposes
    of the summary judgment proceedings that “there is a use of
    state land” in this case and that, therefore, “[t]here is a
    ‘trigger’ pursuant to Haw. Rev. Stat. § 343-5(a) (2010).”              After
    36
    Petitioners also contend that the ICA’s construction of “program”
    and “project” undermines DLNR’s public trust and statutory duties to conserve
    marine resources. In light of our disposition in this case, this issue need
    not be reached.
    37
    The parties’ primary dispute in this case involves whether
    activities allowed under permits issued pursuant to HRS § 188-31 and DLNR’s
    administrative rules are HEPA “actions.” Having found that aquarium
    collection pursuant to permits issued by DLNR is a HEPA “action”--contrary to
    the circuit court’s ruling--we proceed to consider other grounds upon which
    the circuit court’s grant of summary judgment to DLNR may be affirmed. See
    Reyes v. Kuboyama, 76 Hawaii 137, 140–41, 
    870 P.2d 1281
    , 1284–85 (1994)
    (“This court may affirm a grant of summary judgment on any ground appearing
    in the record, even if the circuit court did not rely on it.”). Thus, we
    consider whether there is an issue of material fact as to either of the two
    other requisites of HEPA review.
    46
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    reviewing the applicable legal principles in the discussion that
    follows, we conclude that DLNR’s concession is correct.38
    Categories of land use under which aquarium collection
    may fall include HRS § 343-5(a)(1) (actions that “[p]ropose the
    use of state or county lands”)39 and HRS § 343-5(a)(2) (actions
    that “[p]ropose any use within any land classified as a
    conservation district by the state land use commission under
    chapter 205”).     Therefore, we determine (1) whether marine
    waters40 and the submerged lands in which aquarium collection is
    38
    We review the merits of DLNR’s concession because a court is not
    bound by a party’s “apparent concession of law.” Ass’n of Apartment Owners
    of Newtown Meadows ex rel. its Bd. of Dirs. v. Venture 15, Inc., 115 Hawaii
    232, 254, 
    167 P.3d 225
    , 247 (2007) (citing McCandless v. Campbell, 
    20 Haw. 404
    , 405 (1911)). “[W]e are free to interpret . . . and apply the correct
    law to its enforcement.” Beclar Corp. v. Young, 
    7 Haw. App. 183
    , 190, 
    750 P.2d 934
    , 938–39 (1988).
    39
    In full, HRS § 343-5(a)(1) provides as follows:
    (a) Except as otherwise provided, an environmental
    assessment shall be required for actions that:
    (1) Propose the use of state or county lands or the
    use of state or county funds, other than funds to
    be used for feasibility or planning studies for
    possible future programs or projects that the
    agency has not approved, adopted, or funded, or
    funds to be used for the acquisition of
    unimproved real property; provided that the
    agency shall consider environmental factors and
    available alternatives in its feasibility or
    planning studies; provided further that an
    environmental assessment for proposed uses under
    section 205-2(d)(11) or 205-4.5(a)(13) shall only
    be required pursuant to section 205-5(b) . . . .
    40
    Aquarium collection under HRS § 188-31 also allows extraction of
    fish and other aquatic life from freshwater sources. HRS § 188-31(a). We do
    not address freshwater sources because the activities under the permits being
    challenged in this case, based on the parties’ filings and the record on
    appeal, all transpire in marine waters and submerged lands.
    47
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    conducted constitute state lands or are within a conservation
    district and (2) whether aquarium collection constitutes “use.”
    1. Whether Marine Waters and Submerged Lands in Which Aquarium
    Collection is Conducted Constitute State Lands
    “Land” is not defined by HEPA, so we commence our
    statutory construction by employing “the well-settled canon that
    ‘[l]aws in pari materia, or upon the same subject matter, shall
    be construed with reference to each other.          What is clear in one
    statute may be called upon in aid to explain what is doubtful in
    another.’”    State v. Bovee, 139 Hawaii 530, 544, 
    394 P.3d 760
    ,
    774 (2017) (quoting State v. Alangcas, 134 Hawaii 515, 527, 
    345 P.3d 181
    , 193 (2015)); accord HRS § 1–16 (1993).            Chapter 171 of
    the HRS, the chapter that created DLNR and prescribes its
    authority,41 defines “land” as “includ[ing] all interests therein
    and natural resources including water, minerals, and all such
    things connected with land, unless otherwise expressly
    provided.”    HRS § 171-1 (2011) (emphasis added).          HRS § 171-2
    then defines “public lands” as
    all lands or interest therein in the State classed as
    government or crown lands previous to August 15, 1895, or
    acquired or reserved by the government upon or subsequent
    to that date by purchase, exchange, escheat, or the
    exercise of the right of eminent domain, or in any other
    manner; including lands accreted after May 20, 2003, and
    not otherwise awarded, submerged lands, and lands beneath
    tidal waters that are suitable for reclamation, together
    41
    See generally HRS §§ 171-3 (2011), 171-4 (2011), 171-6 (2011),
    171-7 (2011).
    48
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    with reclaimed lands that have been given the status of
    public lands under this chapter . . . .
    HRS § 171-2 (2011) (emphases added).42
    Thus, included within the meaning of “land” and
    “public lands” are “water” and “submerged lands.”            HRS §§ 171-1,
    171-2.    Based on these definitions, marine waters and submerged
    lands in which aquarium collection is conducted are included
    within the meaning of “land” under HEPA.          HRS §§ 171-1, 171-2.
    Further, when the State acts as a trustee and
    exercises fiduciary duties over certain areas not typically
    considered “state lands,” this court has held that, for HEPA
    purposes, those areas qualify as state lands.           For example, this
    court held that Hawaiian homelands are “state lands” for HEPA
    purposes because of the State’s trust obligations with respect
    to those lands and its fiduciary duty to the beneficiaries of
    those lands.    Kepoo v. Watson, 87 Hawaii 91, 97–98, 
    952 P.2d 379
    , 385–86 (1998).      Similar to the State’s trusteeship to
    Hawaiian homelands, this court has repeatedly reaffirmed that
    42
    On the same note, DLNR’s administrative rules define “[l]and” as
    “all real property, fast or submerged, and all interests therein, including
    fauna, flora, minerals, and all such natural resources, unless otherwise
    expressly provided.” HAR § 13-5-2 (effective 1994). The Land Use
    Commission’s rules define “[l]and” as “all real property in the State
    including areas under water within the boundaries of the State.” HAR § 15-
    15-03 (effective 1997).
    DLNR then defines the phrase “[s]ubmerged lands” as “lands from
    the shoreline seaward to the extent of the State’s jurisdiction.” HAR § 13-
    5-2.
    49
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    the State’s public trust obligations pursuant to article XI,
    section 1 of the Hawaii Constitution extend “to all water
    resources.”   In re Water Use Permit Applications (Waiāhole), 94
    Hawaii 97, 133, 
    9 P.3d 409
    , 445 (2000); Kauai Springs, Inc. v.
    Planning Comm’n of the Cty. of Kauai, 133 Hawaii 141, 172, 
    324 P.3d 951
    , 982 (2014) (“[T]he public trust doctrine applies to
    all water resources without exception or distinction.” (quoting
    Waiāhole, 94 Hawaii at 
    133, 9 P.3d at 445
    )).         The common law of
    Hawaii also embodies the precept that “navigable waters” and
    “[t]he lands under the navigable waters in and around the
    territory of the Hawaiian Government are held in trust for the
    public uses of navigation.”      King v. Oahu Ry. & Land Co., 
    11 Haw. 717
    , 725 (Haw. Terr. 1899).         Just as Hawaiian homelands are
    “state lands” for the purposes of HRS § 343-5(a)(1) because they
    are subject to the State’s statutorily defined trust
    obligations, so too are marine waters and submerged lands, both
    of which are subject to the State’s constitutional and common-
    law public trust duties.      See Kepoo, 87 Hawaii at 
    97–98, 952 P.2d at 385
    –86; Waiāhole, 94 Hawaii at 
    133, 9 P.3d at 445
    .            It
    therefore follows that the State marine waters and the submerged
    lands in which aquarium collection occurs are “state lands”
    under HEPA.
    50
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    2. Whether Marine Waters are Within a Conservation District
    HEPA environmental review is also triggered when an
    action “[p]ropose[s] any use within any land classified as a
    conservation district by the state land use commission under
    chapter 205.”       HRS § 343-5(a)(2).       According to HRS § 205-2(e)
    (Supp. 2012), “[c]onservation districts shall include areas
    necessary for . . . conserving indigenous or endemic . . .
    fish[] and wildlife, including those which are threatened or
    endangered,” or “would maintain or enhance the conservation of
    natural or scenic resources.”           Thus, the legislature uses the
    term “areas” in defining “conservation districts,” and it does
    not limit what constitutes “conservation districts” to “lands.”
    Id.43
    Additionally, pursuant to HRS § 343-5(a)(2), the Land
    Use Commission has adopted HAR § 15-15-20, which provides in
    relevant part the following:
    §15-15-20 Standards for determining “C” conservation
    district boundaries. Except as otherwise provided in this
    chapter, in determining the boundaries for the “C”
    conservation district, the following standards shall apply:
    . . . .
    (6)   It shall include lands having an elevation below the
    shoreline as stated by section 205A-I, HRS, [and]
    marine waters . . . .
    43
    Additionally, as discussed in the preceding section, the term
    “lands” includes “submerged lands” and “waters.”
    51
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    HAR § 15-15-20(6) (effective 1997) (emphases added).            In
    addition, HAR § 15-15-22(a)(2) (effective 1997) provides that in
    interpreting district boundaries, “[l]and having an elevation
    below the shoreline [and] marine waters . . . of the State[] . .
    . shall be included in the conservation district.”            HAR § 15-15-
    22(a)(2) (effective 1997).       Thus, the legislature and the Land
    Use Commission, through its statutory rulemaking authority,
    clearly included lands below the shoreline (i.e., submerged
    lands) and marine waters of the State within conservation
    districts.    See HRS § 205-2(e) (Supp. 2012); HAR § 15-15-20(6);
    HAR § 15-15-22(a)(2).
    The inclusion of State marine waters within
    conservation districts designated by the Land Use Commission is
    reinforced by HRS § 190-1 (2011), which provides that “[a]ll
    marine waters of the State . . . constitute[] a marine life
    conservation area to be administered by the department of land
    and natural resources subject to this chapter and any other
    applicable laws not inconsistent herewith or with any rules
    adopted pursuant hereto.”44       Consistent with its legislative
    mandate, DLNR has promulgated administrative rules that
    44
    Since 1990, the legislature has defined “state marine waters” “as
    extending from the upper reaches of the wash of the waves on shore seaward to
    the limit of the State’s police power and management authority, including the
    United States territorial sea, notwithstanding any law to the contrary.” HRS
    § 190-1.5 (2011).
    52
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    established subzones within conservation districts.45            A
    conservation district, under DLNR rules, encompasses subzones of
    “[l]ands and state marine waters seaward of the shoreline to the
    extent of the State’s jurisdiction, unless placed in a
    [protective] or [limited] subzone.”         HAR § 13-5-13(b)(5)
    (effective 1994) (emphasis added).         Accordingly, lands and State
    marine waters seaward of the shoreline under the State’s
    jurisdiction, in which the aquarium collection practices
    challenged in this case are conducted, are within conservation
    districts classified by the Land Use Commission pursuant to its
    authority under HRS chapter 205 and thus fall within a category
    of land use enumerated in HEPA.
    3. Whether Aquarium Collection is a “Use” Under HRS § 343–5
    We next consider whether aquarium collection is a
    “use” under HRS § 343-5.       “Use” is also an undefined term under
    HEPA, and this court has previously observed that its ordinary
    meaning “could be construed to apply to any ‘use’ of state or
    county land, no matter what or how benign that ‘use’ may be.”
    45
    DLNR’s rulemaking power originates from the legislature, which
    has authorized DLNR to “establish and from time to time modify the limits of
    one or more conservation districts in each county and may, if it deems
    necessary, declare all waters within any county a conservation district.”
    HRS § 190-2 (2011). In addition, the legislature has required DLNR in HRS §
    183C-3(7) (Supp. 1994) to “[e]stablish and enforce land use regulations on
    conservation district lands” and in HRS § 183C-4(b) and (d) (Supp. 1997) to
    “adopt rules governing the use of land within the boundaries of the
    conservation district” and to establish and define zones within the
    conservation district.
    53
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    Nuuanu Valley Ass’n v. City & Cty. of Honolulu, 119 Hawaii 90,
    103, 
    194 P.3d 531
    , 544 (2008).       Our court declined to adopt such
    a sweeping interpretation, concluding “that the boundaries of
    the meaning of the word ‘use,’ as contemplated by HRS § 343–
    5(a)(1), is not unlimited in possibilities.”          
    Id. In reaching
    this conclusion, the court noted that, in a previous case, we
    rejected the plaintiff’s argument “that the ‘potential use of’ a
    public highway leading to [a development] project”
    “constitute[s] use of state land.”        
    Id. (quoting Citizens
    for
    Prot. of N. Kohala Coastline v. Cty. of Hawaii, 91 Hawaii 94,
    103 n.8, 
    979 P.2d 1120
    , 1129 n.8 (1999)).         Thus, this court
    concluded in Nuuanu Valley that merely connecting to an existing
    drainage system and county lines without any construction or
    tunneling beneath state or county lands was not a “use” within
    the meaning of that term in HRS § 343-5(a)(1).          
    Id. at 103—04,
    194 P.3d at 544—45.
    What can be readily gleaned from Nuuanu Valley is that
    whether a proposed activity constitutes a “use of state or
    county lands” depends on the nature of the activity and the
    extent of the involvement of state or county lands.           Id. at 
    103, 194 P.3d at 544
    .    When the proposed activity utilizes state or
    county lands in a decidedly inconsequential or negligible
    manner, like the mere connection to state or county lands in
    Nuuanu Valley, or when the use is hypothetical, like the
    54
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    “potential use” of a public highway in Citizens, then the
    activity does not rise to the level of “use” contemplated by
    HEPA.     When, on the other hand, the proposed activity utilizes
    state or county lands in an actual and more substantial way, the
    activity qualifies as a “use” under HEPA.            Compare Nuuanu
    Valley, 119 Hawaii at 
    103–04, 194 P.3d at 544
    –45 (connecting to
    existing county lines was not a “use”), with Kahana Sunset
    Owners Ass’n v. Cty. of Maui, 86 Hawaii 66, 71, 
    947 P.2d 378
    ,
    383 (1997) (installing a new drainage line beneath a public
    street that would be connected to an existing culvert beneath a
    public highway was a “use”), Citizens, 91 Hawaii at 
    103, 979 P.2d at 1129
    (constructing two underpasses beneath a state
    highway was a “use”), and Sierra Club v. Office of Planning,
    State of Haw., 109 Hawaii 411, 415–16, 
    126 P.3d 1098
    , 1102–03
    (2006) (constructing sewage and water transmission lines by
    tunneling beneath state highways was a “use”).
    Permits for commercial aquarium collection allow for
    the unlimited collection of fish and other aquatic life, and
    each recreational permit authorizes the extraction of close to
    2,000 fish or other aquatic life annually, subject to the terms
    and conditions of the permits and to certain restrictions set by
    law.    See HAR § 13-75-14; 
    see supra
    note 21.           The aquatic life
    collected inhabits “state lands” and conservation districts, as
    55
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    discussed, and are integral components of the State’s reef
    ecosystem.    Thus, aquarium collection utilizes “state lands” and
    conservation districts in an actual and substantial manner.
    Said differently, aquarium collection as allowed under
    commercial and recreational permits cannot be said to fall
    within the narrow spectrum of activities that this court has
    excluded from the meaning of the word “use” in Nuuanu Valley.46
    Accordingly, aquarium collection pursuant to permits issued
    under HRS § 188-31 qualifies as a “use of state . . . lands” and
    as a “use within . . . a conservation district.”47
    C. Whether Aquarium Collection is Exempt under HRS § 343-6(a)(2)
    Having determined that aquarium collection under HRS §
    188-31 and DLNR’s permitting scheme is a HEPA “action” that
    qualifies as a “use of state . . . lands,” we proceed to the
    46
    DLNR argues that, if aquarium collection under HRS § 188-31 is
    considered a HEPA “action,” all activities “in a government building or by a
    government employee” would be subject to environmental review pursuant to
    HEPA because those activities involve “the use of state or county lands or
    the use of state or county funds.” This assertion is without merit because,
    as discussed, not all activities qualify as a “use,” and activities such as
    “turning on the lights” in a government building, a hypothetical that DLNR
    asserts, are unquestionably not within the set of activities that qualify as
    a “use” under Nuuanu Valley.
    47
    As stated, a parent netting one or two fish for recreational use
    would not fall within any of the categories listed in HRS § 343-5(a). See
    supra note 31. The reason is that the nature and magnitude of the
    involvement of marine waters and submerged lands in this type of activity are
    inconsequential and negligible such that this activity would not qualify as a
    “use” of state lands or conservation districts under HRS § 343-5(a). It
    follows that, if permits were issued for activities similarly limited in
    nature and magnitude as a parent collecting one or two fish for recreational
    purposes, the activities under such permits would also not be considered a
    “use” of state and conservation lands.
    56
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    third part of the analysis: whether aquarium collection is
    exempt from HEPA environmental review.          HRS § 343-6 requires the
    Environmental Council to adopt, amend, or repeal rules that
    shall “[e]stablish procedures whereby specific types of actions,
    because they will probably have minimal or no significant
    effects on the environment, are declared exempt from the
    preparation of an environmental assessment.”48             HRS § 343-6(a)(2)
    (2010).    The Environmental Council accordingly adopted
    categories of “actions” in HAR § 11-200-8(a) that “may be
    declared exempt by the proposing agency or approving agency from
    the preparation of an environmental assessment provided that
    48
    HEPA defines “[s]ignificant effect” as
    the sum of effects on the quality of the environment,
    including actions that irrevocably commit a natural
    resource, curtail the range of beneficial uses of the
    environment, are contrary to the State’s environmental
    policies or long-term environmental goals as established by
    law, or adversely affect the economic welfare, social
    welfare, or cultural practices of the community and State.
    HRS § 343-2 (2010).
    HAR § 11-200-2 defines “effects” as follows:
    “Effects” or “impacts” as used in this chapter are
    synonymous. Effects may include ecological effects (such
    as the effects on natural resources and on the components,
    structures, and functioning of affected ecosystems),
    aesthetic effects, historic effects, cultural effects,
    economic effects, social effects, or health effects,
    whether primary, secondary, or cumulative. Effects may
    also include those effects resulting from actions which may
    have both beneficial and detrimental effects, even if on
    balance the agency believes that the effect will be
    beneficial.
    HAR § 11-200-2 (effective 1996).
    57
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    agencies declaring an action exempt under this section shall
    obtain the advice of other outside agencies or individuals
    having jurisdiction or expertise as to the propriety of the
    exemption.”   HAR § 11-200-8(a) (effective 1996).          These
    categories include the operations, repairs, replacement or
    reconstruction of existing structures; construction and
    modification of certain small facilities or structures; minor
    alterations in the conditions of land, water, or vegetation;
    basic data collection and research activities; construction or
    placement of minor structures accessory to existing facilities;
    interior alterations; demolition of certain structures; certain
    zoning variances; continuing administrative activities; and
    acquisition of land and structures for the purpose of affordable
    housing.   
    Id. In addition,
    the Environmental Council decreed by
    administrative rule that “[e]ach agency, through time and
    experience, shall develop its own list of specific types of
    actions which fall within the exempt classes, as long as these
    lists are consistent with both the letter and intent expressed
    in these exempt classes and chapter 343, HRS.”          HAR § 11-200-
    8(d).   The authority of the various agencies under HAR § 11-200-
    8(d), however, is not boundless.         As this court explained in
    Kahana Sunset, the intent of the exemption list in HAR § 11-200-
    8, adopted pursuant to HRS § 343-6(a)(2), is “to exempt only
    58
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    very minor projects from the ambit of HEPA.”          Kahana Sunset
    Owners Ass’n v. Cty. of Maui, 86 Hawaii 66, 72, 
    947 P.2d 378
    ,
    384 (1997).    Thus, this court later held that, when developing
    lists of the exemptions pursuant to HAR § 11-200-8(d), an agency
    must preliminarily determine that the action to be declared
    exempt is a very minor project that “will ‘probably have minimal
    or no significant effects on the environment.’”          Sierra Club v.
    Dep’t of Transp. of the State of Haw., 115 Hawaii 299, 316, 
    167 P.3d 292
    , 309 (2007).      Our decision in Sierra Club also
    concluded “that not only must the exemption list be developed
    with regard to the letter and intent of HEPA and its
    regulations, but so also must individual exemption
    determinations.”     
    Id. This means
    that individual exemption
    determinations must be determined to “probably have minimal or
    no significant effects on the environment.”          
    Id. (quoting HAR
    §
    11-200-2).
    Guided by these principles, this court in Sierra Club
    concluded that an agency must make the following determinations
    in deciding whether a proposed activity is exempt from HEPA.
    Preliminarily, the agency must determine whether the action is
    part of a “group of actions” that must be “treated as a single
    action” pursuant to HAR § 11-200-7 (effective 1985).
    Thereafter, the agency must conduct a four-step analysis: an
    action is exempt from HEPA if (1) it is within an exempt class
    59
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    promulgated by the Environmental Council in HAR § 11-200-8(a) or
    within an exemption category created by the agency itself
    pursuant to its authority under HAR § 11-200-8(d); (2) the
    relevant exemption category can be applied because the activity
    does not have a significant cumulative impact and it does not
    have a significant impact on a particularly sensitive
    environment, see HAR § 11-200-8(b); (3) the agency obtained the
    advice of other agencies or individuals having jurisdiction or
    expertise as to the propriety of the exemption, HAR § 11-200-
    8(a); and (4) the action will probably have minimal or no
    significant effects on the environment, HRS § 343-6(a)(2); see
    also HAR § 11-200-8(d); Sierra Club, 115 Hawaii at 
    315—16, 167 P.3d at 308
    —09.    If the action fails to satisfy any of the four
    requirements discussed, it is not exempt from HEPA.           Sierra
    Club, 115 Hawaii at 
    315—16, 167 P.3d at 308
    —09.
    As a matter of law, it cannot be concluded that
    commercial aquarium collection, which involves the extraction of
    an unlimited number of fish and other aquatic life annually, may
    be exempt from HEPA because it does not qualify within any of
    the exemption categories in HAR § 11-200-8(a).          The most
    relevant exemption--“[m]inor alterations in the conditions of
    land, water, or vegetation” under HAR § 11-200-8(a)(4)--has no
    application because a permit for extraction of an unlimited
    number of aquatic life cannot be said to constitute only a
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    “[m]inor alteration” in the condition of State waters and
    submerged lands.49
    With respect to recreational aquarium collection,
    which allows each permit holder to extract close to 2,000 fish
    or other aquatic life per year,50 the record is not sufficiently
    developed so as to allow this court to determine whether this
    “action” may be exempted from HEPA under an exemption category
    in HAR § 11-200-8(a) or under DLNR’s own exemption list
    promulgated pursuant to HAR § 11-200-8(d).51          In sum, commercial
    49
    With the Environmental Council’s approval, DLNR has promulgated
    its own exemption list pursuant to its authority under HAR § 11-200-8(d).
    Exemption List for the Department of Land and Natural Resources (2015),
    http://oeqc.doh.hawaii.gov/Shared%20Documents/Environmental_Council/Exemption
    _Lists_By_Department/State_Agencies/DLNR_Comprehensive_Exemption_List_06-05-
    15_Final.pdf. None of the exemption classes that DLNR adopted applies in
    this case. The closest relevant exemption under Exemption Class 4--“[m]inor
    alterations in [S]tate waters, including restoration of native species and
    control of invasive weeds, algae, invertebrates, fishes or other invasive
    aquatic organisms”--does not apply because, as discussed, commercial aquarium
    collection cannot be said to constitute a “[m]inor alteration[] in [S]tate
    waters.”
    Because we conclude that activities allowed by commercial
    aquarium collection permits do not qualify under any of the exemption
    categories in HAR § 11-200-8(a) and in DLNR’s own exemption list, it is not
    necessary for this court to apply the other prongs of the exemption framework
    to commercial aquarium collection.
    50
    When the aquarium collector does not collect the maximum amount
    of aquatic animals authorized, the catch could be such that rarer, more
    vulnerable species are specifically targeted.
    51
    A parent collecting one or two fish for recreational use, aside
    from not falling within any of the categories under HRS § 343-5(a), may also
    be exempt from HEPA. See supra note 31. This is because this activity
    arguably falls under the exemption for minor alterations in the conditions of
    land, water, or vegetation, as discussed in this section. Thus, if permits
    issued under HRS § 188-31 allow only activities similar in nature and
    magnitude as a parent collecting one or two fish for recreational purposes,
    the activity may also be exempt from HEPA within the framework discussed
    above.
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    aquarium collection is not exempted from HEPA, but the
    possibility that recreational aquarium collection as authorized
    under HRS § 188-31 and DLNR’s administrative rules may be
    exempted should be explored further by the parties and the
    circuit court upon remand using the analytical framework
    discussed herein.
    D. Discretionary Consent
    We have determined that aquarium collection is a HEPA
    “action” that qualifies as a use of state lands and that, while
    commercial aquarium collection is not exempted from HEPA’s
    environmental review requirements, the record is not
    sufficiently developed for this court to determine whether the
    same is true for recreational aquarium collection.           However,
    because aquarium collection has been cast in this case as an
    applicant action, in order for environmental review to be
    required under HEPA, there is an additional inquiry of whether
    issuing a permit for aquarium collection requires “approval of
    an agency.”   HRS § 343-5(e) (Supp. 2012).52
    52
    In relevant part, HRS § 343-5(e) provides as follows:
    (e)    Whenever an applicant proposes an action
    specified by subsection (a) that requires approval of an
    agency and that is not a specific type of action declared
    exempt under section 343-6, the agency initially receiving
    and agreeing to process the request for approval shall
    require the applicant to prepare an environmental
    assessment of the proposed action at the earliest
    (continued . . .)
    62
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    “Approval,” as defined by HEPA, “means a discretionary
    consent required from an agency prior to actual implementation
    of an action.”      HRS § 343-2 (2010).     “‘Discretionary consent’
    means a consent, sanction, or recommendation from an agency for
    which judgment and free will may be exercised by the issuing
    agency, as distinguished from a ministerial consent.”                
    Id. DLNR contends
    that it does not issue an “approval” because it does
    not exercise discretion whenever it issues aquarium collection
    permits pursuant to HRS § 188-31 (2011) and that, therefore,
    HEPA does not apply to aquarium collection.
    (continued . . .)
    practicable time to determine whether an environmental
    impact statement shall be required . . . .
    HRS § 343-5(e) (emphasis added).
    In their reply, Petitioners argue that the ICA’s holding
    regarding DLNR’s discretionary authority is not properly before this court
    because DLNR did not cross-file an application for writ of certiorari
    challenging that portion of the ICA’s published opinion. However, whether
    discretionary authority exists is a “subsidiary question fairly comprised” by
    the issue presented in Petitioners’ application for writ of certiorari--
    whether aquarium collection pursuant to HRS § 188-31 and DLNR’s
    administrative rules requires HEPA review--because, as explained, in order to
    ultimately resolve the issue presented, this court must determine whether
    DLNR exercises discretionary consent in granting HRS § 188-31 aquarium
    permits. Hawaii Rules of Appellate Procedure (HRAP) Rule 40.1(d)(1) (2016)
    (“The statement of a question presented will be deemed to include every
    subsidiary question fairly comprised therein.”). In addition, we reach the
    question of discretionary authority as part of our duty to consider any
    grounds upon which the circuit court’s summary judgment ruling may be
    affirmed. See supra note 37.
    63
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    HRS § 188-31 expressly provides that DLNR, “upon
    receipt of a written application, may issue an aquarium fish
    permit, not longer than one year in duration, to use fine meshed
    traps, or fine meshed nets other than throw nets, for the taking
    of marine or freshwater nongame fish and other aquatic life for
    aquarium purposes.”53     HRS § 188-31(a) (emphasis added).          “The
    term ‘may’ is generally construed to render optional,
    53
    As stated, HRS § 188-31 provides the following:
    (a)   Except as prohibited by law, the department,
    upon receipt of a written application, may issue an
    aquarium fish permit, not longer than one year in duration,
    to use fine meshed traps, or fine meshed nets other than
    throw nets, for the taking of marine or freshwater nongame
    fish and other aquatic life for aquarium purposes.
    (b)   Except as prohibited by law, the permits shall
    be issued only to persons who can satisfy the department
    that they possess facilities to and can maintain fish and
    other aquatic life alive and in reasonable health.
    (c)   It shall be illegal to sell or offer for sale
    any fish and other aquatic life taken under an aquarium
    fish permit unless those fish and other aquatic life are
    sold alive for aquarium purposes.
    The department may adopt rules pursuant to chapter 91
    for the purpose of this section.
    (d) For the purposes of this section:
    (1) “Aquarium purposes” means   to hold salt water
    fish, freshwater nongame   fish, or other aquatic
    life alive in a state of   captivity as pets, for
    scientific study, or for   public exhibition or
    display, or for sale for   these purposes; and
    (2) “Aquarium fish permit” means a permit issued by
    the board for the use of fine mesh nets and
    traps to take salt water fish, freshwater
    nongame fish, or other aquatic life for
    aquarium purposes.
    HRS § 188-31 (emphases added).
    64
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    permissive, or discretionary the provision in which it is
    embodied; this is so at least when there is nothing in the
    wording, sense, or policy of the provision demanding an unusual
    interpretation.”    State v. Kahawai, 103 Hawaii 462, 465, 
    83 P.3d 725
    , 728 (2004) (quoting State ex rel. City of Niles v. Bernard,
    
    372 N.E.2d 339
    , 341 (Ohio 1978)).        Where “may” and “shall” “are
    used in the same statute, especially where they are used in
    close juxtaposition, we infer that the legislature realized the
    difference in meaning and intended that the verbs used should
    carry with them their ordinary meanings.”         State v. Cornelio, 84
    Hawaii 476, 493, 
    935 P.2d 1021
    , 1038 (1997) (quoting Gray v.
    Admin. Dir. of the Court, State of Haw., 84 Hawaii 138, 149, 
    931 P.2d 580
    , 591 (1997)).     In such instances, “the close proximity
    of the contrasting verbs ‘may’ and ‘shall’ requires a non-
    mandatory, i.e., a discretionary, construction of the term
    ‘may.’”    
    Id. (quoting Gray
    , 84 Hawaii at 
    149, 931 P.2d at 591
    ).
    In HRS § 188-31, “may” is used in subsection (a),
    where DLNR is given the authority to issue aquarium collection
    permits.    The verb “shall” is then used in subsection (b), which
    provides that “the permits shall be issued only to persons who
    can satisfy the department that they possess facilities to and
    can maintain fish and other aquatic life alive and in reasonable
    health.”    HRS § 188-31(b).    The verbs “shall” and “may” are both
    65
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    used in subsection (c), which states that “[i]t shall be illegal
    to sell or offer for sale any fish and other aquatic life taken
    under an aquarium fish permit unless those fish and other
    aquatic life are sold alive for aquarium purposes” and that
    “[t]he department may adopt rules pursuant to chapter 91 for the
    purpose of this section.”      HRS § 188-31(c).      Thus, the verbs
    “may” and “shall” are used “in close juxtaposition” in HRS §
    188-31, and the legislature should be presumed to have done so
    deliberately and with full knowledge of the difference between
    the ordinary significations of these verbs.          Cornelio, 84 Hawaii
    at 
    493, 935 P.2d at 1038
    .      As such, the use of the verb “may” in
    subsection (a) “render optional, permissive, or discretionary”
    DLNR’s statutory authority to issue aquarium collection permits
    pursuant to HRS § 188-31.      Kahawai, 103 Hawaii at 
    465, 83 P.3d at 728
    .
    HRS § 188-31(b) provides further indication that DLNR
    possesses the authority to exercise discretionary consent in the
    aquarium collection permitting process.         Subsection (b) of HRS §
    188-31 provides that “the permits shall be issued only to
    persons who can satisfy the department that they possess
    facilities to and can maintain fish and other aquatic life alive
    and in reasonable health.”      HRS § 188-31(b) (emphasis added).
    Accordingly, HRS § 188-31(b) explicitly allows DLNR to exercise
    its independent judgment in determining whether a permit
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    applicant possesses facilities to and can maintain fish and
    other aquatic life alive and in reasonable health.           See HRS §
    343-2 (defining discretionary consent as “a consent, sanction,
    or recommendation from an agency for which judgment and free
    will may be exercised by the issuing agency, as distinguished
    from a ministerial consent”).       If DLNR is not satisfied that a
    permit applicant has the ability to comply with the provisions
    of HRS § 188-31(b), DLNR has the statutory discretion not to
    issue an aquarium collection permit.        Not only does DLNR
    exercise its independent judgment pursuant to HRS § 188-31(b),
    DLNR is also authorized, under HRS § 188-31(c), to adopt
    administrative rules to effectuate the aquarium collection
    permitting scheme.    HRS § 188-31(c).      As the ICA also
    recognized, the legislative history of HRS § 188–31 makes DLNR’s
    discretionary authority clear, as the statute “provides
    safeguards so that the abuse of the privilege of using fine mesh
    nets can be prevented.”     Umberger v. Dep’t of Land & Nat.
    Resources, 138 Hawaii 508, 518, 
    382 P.3d 320
    , 330 (App. 2016)
    (emphasis omitted) (quoting H. Stand. Comm. Rep. No. 586, in
    1953 House Journal, at 675).      Thus, there is no merit to DLNR’s
    argument that it does not possess the authority to exercise
    discretionary consent in the aquarium collection permitting
    process.
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    DLNR further argues that it does not exercise
    discretion in issuing aquarium collection permits because “[t]he
    application process is on-line and completely automatic.”
    However, the fact that DLNR has chosen not to exercise its
    discretion under the plain and unambiguous language of HRS §
    188-31 does not nullify the statute’s clear directive that DLNR
    is given the authority to exercise discretionary consent.             An
    agency may not defeat the express provisions of a statute simply
    by operating in a manner that does not comport with the
    legislature’s grant of authority.        See Hyland v. Gonzales, 139
    Hawaii 386, 382, 
    390 P.3d 1273
    , 1279 (2017) (concluding that the
    local election board’s interpretation of its regulation must be
    consistent with the act being administered and that the board
    cannot contradict the statute that it is attempting to
    implement).   This would also be contrary to the principle,
    recognized by a majority of this court, that “[a]n agency is a
    creature of the legislature, and the scope of its authority is
    specifically delineated by statute.”        Mauna Kea Anaina Hou v.
    Bd. of Land & Nat. Res., 136 Hawaii 376, 413 n.14, 
    363 P.3d 224
    ,
    261 n.14 (2015) (Pollack, J., concurring).
    To conclude, DLNR’s challenge to the ICA’s holding
    that DLNR has discretionary consent is without merit.            Thus,
    aquarium collection pursuant to permits issued under HRS § 188-
    31 is an applicant action that requires agency approval.
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    E. Summary Judgment
    The circuit court granted DLNR’s motion for summary
    judgment and, correspondingly, denied Petitioners’ summary
    judgment motion upon concluding that aquarium collection under
    HRS § 188-31 (2011) is not a HEPA “action.”          This court’s
    framework in reviewing decisions regarding summary judgment is
    as follows:
    [S]ummary judgment is appropriate if the pleadings,
    depositions, answers to interrogatories, and admissions on
    file, together with the affidavits, if any, show that there
    is no genuine issue as to any material fact and that the
    moving party is entitled to judgment as a matter of law. A
    fact is material if proof of that fact would have the
    effect of establishing or refuting one of the essential
    elements of a cause of action or defense asserted by the
    parties. The evidence must be viewed in the light most
    favorable to the non-moving party. In other words, we must
    view all of the evidence and the inferences drawn therefrom
    in the light most favorable to the party opposing the
    motion.
    Lambert v. Waha, 137 Hawaii 423, 432 n.9, 
    375 P.3d 202
    , 211 n.9
    (2016) (quoting Querubin v. Thronas, 107 Hawaii 48, 56, 
    109 P.3d 689
    , 697 (2005)).    The burden is on the moving party “to show
    the absence of any genuine issue as to all material facts,
    which, under applicable principles of substantive law, entitles
    the moving party to judgment as a matter of law.”           French v.
    Haw. Pizza Hut, Inc., 105 Hawaii 462, 470, 
    99 P.3d 1046
    , 1054
    (2004) (quoting GECC Fin. Corp. v. Jaffarian, 79 Hawaii 516,
    521, 
    904 P.2d 530
    , 535 (App. 1995)).        Only after the moving
    party satisfies its initial burden would the burden shift to the
    69
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    nonmoving party to “demonstrate specific facts, as opposed to
    general allegations, that present a genuine issue worthy of
    trial.”   
    Id. (emphasis omitted)
    (quoting GECC Fin. Corp., 79
    Hawaii at 
    521, 904 P.2d at 535
    ).
    Because aquarium collection pursuant to commercial and
    recreational permits issued by DLNR is a HEPA “action,” the
    circuit court erred in granting DLNR’s motion for summary
    judgment on the basis that aquarium collection is not a HEPA
    “action.”    The circuit court also erred to the extent that it
    denied Petitioners’ summary judgment motion with respect to
    commercial aquarium collection permits because, as discussed,
    the authorized conduct under such permits is an applicant
    “action” under HEPA, is a use of state lands and a use within a
    conservation district, is not exempted from HEPA, and is subject
    to DLNR’s discretionary consent.         Thus, the conduct allowed
    under commercial aquarium collection permits, issued pursuant to
    HRS § 188-31 and DLNR’s administrative scheme, is subject to
    HEPA environmental review, and there is no genuine issue of
    material fact as to this issue.       To the extent that the circuit
    court did not grant Petitioners’ summary judgment motion with
    respect to recreational aquarium collection permits, it did not
    err because the record is not sufficiently developed so as to
    allow the circuit court to determine whether activities allowed
    under recreational permits may be exempted from HEPA
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    environmental review.     In other words, there was a genuine issue
    of material fact as to whether activities authorized by
    recreational permits are subject to HEPA review.
    In summary, the circuit court erred in granting DLNR
    summary judgment and in denying Petitioners’ summary judgment
    motion with respect to commercial aquarium collection permits.
    The circuit court did not err in denying Petitioners’ motion for
    summary judgment with respect to recreational aquarium
    collection permits.
    We note that HRS § 343-5(g) (Supp. 2012) provides that
    agencies, in preparing an environmental assessment, “may
    consider and, where applicable and appropriate, incorporate by
    reference, in whole or in part, previous determinations of
    whether a statement is required and previously accepted
    statements.”   HRS 343-5(g) (Supp. 2012).        A similar authority,
    derived from HRS § 343-5, exists in HAR § 11-200-13(a)
    (effective 1996), providing “that whenever an agency proposes to
    implement an action or receives a request for approval, the
    agency may consider and, when applicable and appropriate,
    incorporate by reference, in whole or in part, previous
    determinations of whether a statement is required, and
    previously accepted statements.”         These provisions alleviate the
    concern that an environmental assessment would necessarily have
    to be prepared whenever an applicant applies for an aquarium
    71
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    collection permit.    Further, “a group of proposed actions may be
    treated by a single environmental assessment or statement,” HRS
    § 343-6(a)(1) (2010), when “[t]he actions in question are
    essentially identical and a single statement will adequately
    address the impacts of each individual action and those of the
    group of actions as a whole,” HAR § 11-200-7 (effective 1985).
    Such an approach can assuage concerns about aquarium collectors
    not having the resources to comply with HEPA.
    On remand, the circuit court is directed to grant
    Petitioners’ summary judgment motion to the extent that
    Petitioners are requesting declaratory relief and a prohibitory
    injunction as to commercial aquarium collection pursuant to
    permits issued under HRS § 188-31 and DLNR’s administrative
    rules.   Further proceedings are necessary, however, in order to
    determine whether Petitioners are entitled to declaratory relief
    and a prohibitory injunction as to recreational aquarium
    collection permits.
    VI. CONCLUSION
    Accordingly, we vacate the ICA’s judgment insofar as
    it affirmed the circuit court’s judgment granting DLNR summary
    judgment.    The ICA’s judgment is further vacated to the extent
    that it affirmed the circuit court’s judgment denying
    Petitioners’ motion for summary judgment with respect to
    commercial aquarium collection permits.         Similarly, the circuit
    72
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    court’s judgment is vacated insofar as it granted summary
    judgment to DLNR and denied Petitioners’ summary judgment motion
    with respect to commercial aquarium collection permits.            The
    remaining portions of the judgments of the ICA and the circuit
    court are otherwise affirmed, and this case is remanded to the
    circuit court for further proceedings consistent with this
    opinion.
    Paul H. Achitoff and                     /s/ Mark E. Recktenwald
    Summer Kupau-Odo
    for petitioners                          /s/ Paula A. Nakayama
    /s/ Sabrina S. McKenna
    William J. Wynhoff
    for respondent                           /s/ Richard W. Pollack
    /s/ Michael D. Wilson
    73
    

Document Info

Docket Number: SCWC-13-0002125

Citation Numbers: 140 Haw. 500, 403 P.3d 277

Judges: Recktenwald, Nakayama, McKenna, Pollack, Wilson

Filed Date: 9/6/2017

Precedential Status: Precedential

Modified Date: 11/8/2024

Authorities (23)

Kepo'o v. Kane , 106 Haw. 270 ( 2005 )

Querubin v. Thronas , 107 Haw. 48 ( 2005 )

State v. Cornelio , 84 Haw. 476 ( 1997 )

Waikiki Resort Hotel, Inc. v. City & County of Honolulu , 63 Haw. 222 ( 1981 )

Beclar Corp. v. Young , 7 Haw. App. 183 ( 1988 )

Unite Here! Local 5 v. City & County of Honolulu , 123 Haw. 150 ( 2010 )

Gray v. Administrative Director of Court , 84 Haw. 138 ( 1997 )

Sierra Club v. OFFICE OF PLANNING, STATE , 109 Haw. 411 ( 2006 )

Life of the Land v. Ariyoshi , 59 Haw. 156 ( 1978 )

State v. Kahawai , 103 Haw. 462 ( 2004 )

McGlone v. Inaba , 64 Haw. 27 ( 1981 )

Citizens for the Protection of the North Kohala Coastline ... , 91 Haw. 94 ( 1999 )

Medeiros v. Hawaii County Planning Commission , 8 Haw. App. 183 ( 1990 )

Nuuanu Valley Ass'n v. City & County of Honolulu , 119 Haw. 90 ( 2008 )

MOLOKAI HOMESTEADERS CO-OP. ASS'N v. Cobb , 629 P.2d 1134 ( 1981 )

Franks v. City and County of Honolulu , 74 Haw. 328 ( 1993 )

In Re Water Use Permit Applications , 94 Haw. 97 ( 2000 )

Price v. Obayashi Hawaii Corp. , 81 Haw. 171 ( 1996 )

Kahana Sunset Owners Ass'n v. County of Maui , 86 Haw. 66 ( 1997 )

Waianae Coast Neighborhood Board v. Hawaiian Electric Co. , 64 Haw. 126 ( 1981 )

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