Rising Sea Level Due to Climate Change in Playa Grande, Las Baulas National Park, Costa Rica - Drews & Fonseca 2009

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  • 8/14/2019 Rising Sea Level Due to Climate Change in Playa Grande, Las Baulas National Park, Costa Rica - Drews & Fonsec

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    Carlos Drews & Ana Fonseca

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    Produced by Communications Department

    WWF Central America

    2009

    Graphic Design:

    Jeffrey Muoz

    Production:

    Zeidy HidalgoMarianne Fish

    Carlos Drews

    Ana Fonseca

    Edition:

    Carlos Drews

    Ana Fonseca

    Translation:

    Lucinda Taft

    Cover Photo:Aerial photograph of Playa Grande, Las Baulas National Park, taken on May 1st, 2009 .

    Carlos DREWS / WWF

    Cite as:

    Fonseca, A. & C. Drews. 2009. Rising sea level due to climate change at Playa Grande,

    Las Baulas National Park, Costa Rica: inundation simulation based on a high resolution, digital elevation model and

    implications for park management. WWF / Stereocarto Report, San Jos, pp. 20.

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    Summary

    Flooding models under dierent sea-level rise

    scenarios are needed to better plan or coastal

    development and protected areas, in a way such

    that both marine turtles and local communities

    beneft. Playa Grande, the most important nest-

    ing site o the Eastern Pacifc or the critically

    endangered leatherback turtle, is located in Las

    Baulas National Park, Costa Rica. It is realisticto expect a 1 m sea-level rise by the end o

    the century due to climate change. This would

    imply a 50 m retreat o the beach landwards.

    Additionally, the high-resolution, digital eleva-

    tion model reveals that or the most part the

    inundation o the Playa Grande area will occur

    rom behind. As sea level rises, the water will

    advance through the mouth o the Tamarindo

    estuary, and into the surrounding wetlands, in-

    undating part o the land bordering the current

    mangroves. The uture o Playa Grande depends

    on its ability to retreat as sea level rises and

    at the same time maintain adequate ecological

    conditions or the nesting o leatherbacks. This

    implies that existing and uture inrastructure

    does not hinder the retreat o the beach and that

    the buer zone o the national park warrants e-

    ective environmental mitigation measures in

    the light o the uture locations o the beach

    and o the retreat o the mangroves. The law

    proposal to rectiy the boundaries o the park

    that would reduce its width to a ringe o 50 m

    would imply that the park would be underwater

    by the end o the century. The beach would be

    located inside the proposed wildlie reuge and

    turtles and their nests would compete or space

    with houses and other inrastructure. Once the

    beach retreats against the inrastructure, the

    wave action against roads and buildings will

    cause erosion and, consequently, loss o nest-

    ing area. In relation to rising sea levels, the pro-

    posal to rectiy the boundaries o the national

    park is shortsighted and not precautionary. It

    would compromise in the mid- and long-term

    its ecological role as leatherback nesting area,

    and as such, the very reason or the creation o

    this particular park. Implementation o adapta-

    tion measures to counter the impacts o climatechange in turtle nesting beaches is an interna-

    tional commitment under the Inter-American

    Convention or Marine Turtle Protection and

    Conservation, to which Costa Rica is a signatory

    party. With the implementation o such mea-

    sures, Costa Rica has the opportunity to main-

    tain its regional leadership in the conservation

    o marine turtles and its status as a world-class

    reerence in biodiversity conservation.

    Inundation simulation based on a high

    resolution, digital elevation model and

    implications for park management

    Carlos Drews and Ana Fonseca

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    Results and discussion

    Simulation o the inundation o Playa Grande

    One important preliminary step toward the denition

    o adaptation measures or sea level rise and globa

    warming due to climate change are accurate loca

    inundation models that take the greatest number o

    atmospheric, terrestrial and oceanographic variables

    into account. Inundation modeling is a complex process that involves several analytical stages o the

    marine-coastal and atmospheric dynamic. As a rs

    stage, a digital land model was generated using LI-

    DAR technology, an aerial sensor that scanned the

    beach with laser beams, yielding high-resolution data

    on topographical elevation. A possible inundation was

    simulated statically based on this topography, ortho

    photography and dierent sea level rise scenarios (0

    to 150 cm)8. These simulations, images and maps are

    useul tools or raising awareness and helping gov

    ernmental and civil society decision makers plan the

    incorporation o sea level rise into protected area and

    coastal development management. The next stage o

    this project will gather and add data on wave action

    tides, bathymetry, currents, tectonics, precipitation

    temperature, and more to the topographic data, to

    analyze a wide range o vulnerabilities and generate

    a more accurate, dynamic model o beach movemen

    and inundation due to the impact o climate change

    on these beaches.

    According to the most recent estimates o a one-meter sea-

    level rise anticipated or the end o the century, the beach

    at Playa Grande will retreat some 50 meters during this

    period 9, as the beach is pushed landwards by wave actio

    as the sea level rises. Under this assumption, Figure 9 rep

    resents the landward displacement o the beach, relative to

    the current tide line. The public zone o 50 meters and the

    maritime-terrestrial zone will gradually shit landwards too

    I there were buildings in this zone, in the uture nesting

    turtles would compete directly or space with houses and

    other inrastructure as the beach shited to surround those

    buildings. In theory, this could turn out to be the case with

    regards to some o the buildings now in existence (Fig. 10)

    although it is unknown whether the nesting zone preerred

    by the leatherbacks will include these specic stretches o

    8 Modications to the littoral zone during the periodcontemplated in the simulation are not illustrated. This

    simulation is also known as a bathtub model o sea leve

    rise. It does not take the retreat o the beach as sea leve

    rises into account.

    9 Source: Daz-Andrade, J.M. 1996,Anlisis de la

    vulnerabilidad de la zona costera ante el ascenso de

    nivel del mar por un cambio climtico global Costa

    del Pacfco de Costa Rica, Inorme fnal del Proyecto

    Centroamericano sobre Cambio Climtico, Comit Re

    gional de Recursos Hidrulicos. San Jos, Costa Rica

    ever, we also discuss the management implications o

    projections or beach retreat based on published ac-

    counts by other authors. A subsequent stage is expect-

    ed to generate a dynamic model o the inundation that

    also considers bathymetry, wave action and the littoral

    zones response in shape and size. The latter will allow

    calculation o eventual reorientations o the beach in the

    uture and the range o extreme storm surges.

    Methodology

    Playa Grande beach is approximately 4.3 km long with

    white sand, located in Guanacaste province. Its geo-

    graphic coordinates are: northern end 10 20 44 N,

    85 51 37 W and southern end 10 18 30 N, 85

    50 11 W. The beach is protected within Las Baulas

    Marine Park that also includes Ventanas, Langosta and

    Carbn beaches, the San Francisco and Tamarindo es-

    tuaries, and 125 m landward rom the regular high tide

    line. Leatherbacks nest mainly in the center o the beach

    where there is very little inrastructure at present.

    On June 6, 2009, a fy-over o Playa Grande and Junquil-

    lal Beach was done in a Piper Azteca PA-23-250 aircrat,

    equipped or fights with simultaneous LIDAR and digital

    photography technology. Flight hours or Playa Grande

    were 08:04 to 08:16 am and or Junquillal rom 08:21 to

    08:28 am, which determines the tide level shown in the

    photographs. At the time o the overfight on that day, low

    tide was at 7.35 h (46 cm) and high tide was at 13.52 h

    (265 cm) in Puntarenas as a point o reerence. Thus, the

    photographs portray low tide conditions. During the fight

    laser data were captured with a LIDAR Leica ALS 50 II

    sensor or generating the Digital Terrain Models (DTM,

    see Fig. 4) and Digital Surace Models (DSM) rom the

    lowest low tide point to 500 m landward, with a resolution

    o 4 to 5 points/meter2 and an altitudinal precision o 15

    cm. Additionally, aerial photos were taken on a 1:30,000

    scale with a medium ormat RCD 105 digital camera that

    were then ortho-rectied (Figs. 3, 5-10). The images

    were integrated into a tridimensional vision system called

    Stereocaptor to produce animations7 o the possible in-

    undation o Playa Grande under dierent sea level rise

    scenarios (rom 0 to 150 cm, every 10 cm).

    The anticipated 50-m retreat o the beach landward has

    not been refected in the simulations o simple inunda-tions. In order to illustrate this retreat, the orthophoto-

    graph o the uture scenario in Figure 8 was edited us-

    ing Adobe Photoshop, moving the beach landward and

    maintaining current building locations as points o reer-

    ence. In Figures 9 and 10, lines are used to indicate the

    modied boundaries o the beach as a consequence o

    their eventual uture displacement.

    7 These animations are not included in this report

    and are distributed by WWF upon request.

    sures. This report graphically presents the results o

    simple models to simulate inundation due to sea level

    rise at Playa Grande and it mentions the implications

    o the expected landward retreat o the beach or the

    management o the national park.

    Purpose and scope o this study

    Massive hotel development and the parceling o real

    estate or condominiums are exerting major ecosys-tem pressures in Guanacaste province that are most

    intensive on the coastal-marine environments, where

    aquiers, wetlands and mangroves are being aected.

    The main challenge at Playa Grande is to achieve en-

    vironmental compatibility o present and uture coastal

    development with the ecological unction o the national

    park. Some properties are still held within the park

    boundaries and the government as per the correspond-

    ing legal ruling should expropriate these. A drat law

    has been submitted by the Presidency o the Republic

    or the consideration o the Legislative Assembly that

    proposes a reduction in the width o the park in order

    to exclude these properties rom the area o maximum

    protection and avoid the extensive costs o the expro-

    priation. WWF has expressed its opposition to this drat

    law based on considerations o the implications o sea

    level rise, arguments that up until now did not gure

    in the debate. Furthermore, a technical document rom

    SETENA is in preparation about the park buer zone

    (500 m wide, see Fig. 9) that will recommend mitiga-

    tion measures or the environmental impact on the park

    o development. Construction permits have been para-

    lyzed in this zone until the Constitutional Court makes a

    ruling on SETENAs recommendations. Consideration o

    sea level rise is pertinent in these processes because

    this will determine the location and condition o the

    beach in the medium and long term.

    The purpose o this study is to generate inundation

    simulations or some scenarios o sea level rise due to

    climate change, which can be used to raise awareness

    in coastal communities about this problem and aid the

    management authorities o protected wildlands in de-

    signing inrastructure-ree setbacks that will allow Las

    Baulas National Park to ulll its ecological unction in

    the long term. We made a tridimensional, high-reso-

    lution digital land model o Playa Grande using LIDAR

    technology6

    . At this stage the study has been limited togenerating a simple bath tub fooding simulation or

    the sea level rise projected or the end o the century,

    based on detailed topography o the littoral zone. How-

    6 LIDAR (Light Intensity Detection and Ranging):

    This is an active laser system that works in the visible,

    ultraviolet and near inrared spectrum. It has applica-

    tions in studies o the atmosphere and as an altimeter

    in overfights that generate very accurate digital eleva-

    tion models.

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    a periodic record should be made o the distance

    rom several points on the beach to xed points on the

    coast, such as buildings and boundary markers These

    records are necessary or designing the inclusion o set-

    backs (zones behind the beach with no inrastructure

    in land-use regulatory plans as an adaptation measure

    to sea level rise. Las Baulas National Park has still not

    designed the setbacks that are technically necessary to

    compensate or sea level rise, such that the beach can

    retreat landward and continue exercising its unction asthe most important nesting site o the Eastern Pacic o

    leatherbacks, a critically endangered species.

    The setback zone is essential to maintain the integri

    ty o the coastal vegetation strip, which will also shi

    arther inland; the vegetation unctions as a natura

    barrier or mitigating the eects o articial lighting

    rom buildings that disorients the turtles, and also

    provides shade that can reduce the probability o

    nest overheating13. Furthermore, prudent setbacks

    must also be established to allow the gradual retrea

    o this parks mangroves without harming their eco

    logical unction. National parks should be designed

    to ull their protective unction long-term. WWF is

    preparing to work in coordination with SINAC and the

    authorities o Las Baulas precisely to address this

    challenge.

    International commitment to adaptation to

    climate change

    In April 2009, during the 4th Conerence o the Par

    ties to the Inter-American Convention or the Protec

    tion and Conservation o Sea Turtles held in San Jos

    the government o Costa Rica (a signatory nation

    proposed resolution CIT-COP4-2009-R5 Adaptatio

    o sea turtle habitats to climate change, which was

    approved by consensus. This trailblazing resolution

    urges signatory nations to design, identiy and imple

    ment stronger corrective measures and adaptations

    to climate change in management plans, regulatory

    plans, and programs or the protection and conserva

    tion o sea turtles and their habitats, among others

    The implementation o corrective and adaptation mea

    sures is an international commitment, in which Costa

    Rica is already showing clear leadership with regard to

    sea turtles, as demonstrated by the conservation proj

    ect at Junquillal Beach where adjustments in management are now being implemented on the beach to

    mitigate the impacts o climate change. This kind o

    initiative is pending or Las Baulas National Park and

    the other Costa Rican nesting beaches o regional and

    global importance.

    13 Measurements made by WWF at Junquillal Beac

    indicate that the coastal vegetation strip can reduce in

    cubation temperature by 2-3 degrees Centigrade along

    the higher elevation stretch o the beach.

    ta Rica, spring tides can reach up to 1 m above the level

    o ordinary high tides12. This preliminary fooding simula-

    tion does not refect that a 1-meter sea level rise by the

    end o the century, considered realistic by the scientic

    community, would probably also completely inundate the

    50-meter strip o the current public zone. Figure 8 re-

    constructs the eventual location o the beach by the end

    o the century, displaced some 50 m landward, and it

    illustrates how some buildings would be immersed on the

    beach (also see Figs. 9 and 10). The estimated 50-me-ter retreat o the beach by the end o the century due to

    sea level rise means that the current public zone will be

    totally submerged by that time (Fig. 9). The drat law or

    rectiying the boundaries o Las Baulas National Park11

    (in review by the Permanent Special Commission or the

    Environment o the Legislative Assembly) would reduce

    the park to this 50-meter strip, condemning it to be under

    water in the uture and, thus, to disappear by the end

    o the century. In addition will be completely within the

    proposed wildlie reuge, in immediate confict or space

    with buildings and other inrastructure. Under these con-

    ditions, the ecological unction o the beach as a leather-

    back-nesting site would be seriously compromised.

    Figures 8, 9 and 10 are approximations o the possi-

    ble impact o the retreat o the beach due to sea level

    rise but this estimate could be made more accurate in

    a one-to-two year investigation o Las Baulas National

    Park10 that would consider the evolution o wave ac-

    tion, winds, tides and the topography under climate

    change scenarios in a way that would also refect the

    intrusion o peak high tides, to generate a dynamic in-

    undation model with probability levels or normal and

    extreme events. Inrastructure-ree setbacks must be

    designed to reduce the vulnerability o the investments

    in coastal development to the fooding due to rising

    sea level and so as not to block the ormation o new

    beach inland, thus maintaining conditions suitable or

    nesting sea turtles. Such setbacks are a undamental

    tool in sea turtle conservation, particularly in the con-

    text o adaptation to climate change12.

    Inrastructure-ree setbacks to compensate

    or sea level rise

    The Manual sobre tcnicas de manejo y conservacin

    de las tortugas marinas en playas de anidacin de Cen-

    troamrica, published in 2008 by the Inter-AmericanConvention or the Protection and Conservation o Sea

    Turtles, o which Costa Rica is a member, indicates that

    11 Expediente No. 17.383, Recticacin de Lmites

    del Parque Nacional Marino Las Baulas y Creacin del

    Reugio de Vida Silvestre Las Baulas de Propiedad Mixta

    12 Fish M.R., I.M. Ct, J.A. Horrocks, B. Mulligan, A.R.

    Watkinson and A.P. Jones. 2008. Construction setback

    regulations and sea-level rise: mitigating sea turtle nesting

    beach loss. Ocean and Coastal Management 51:330-341.

    the beach in the uture. However, once the beach reaches

    the inrastructure, wave action on roads and/or buildings

    will cause erosion and loss o beach area. In Bonaire, or

    example, it is estimated that 32% o the beach area will be

    lost with a sea level rise o 50 cm, due to the inrastruc-

    ture and natural obstacles that would impede the gradual

    retreat o the beach10. It is essential that the current size

    o Las Baulas National Park is maintained and buer zone

    measures are dened to compensate or beach displace-

    ment so that the park best ullls its ecological unction inthe short as well as the long term.

    According to the preliminary simulation or a 1-meter

    sea level rise, it is very probable that a large part o the

    inundation o the Playa Grande zone would occur rom

    behind, as sea level rises and water advances via the

    mouth o the Tamarindo estuary and the surrounding

    wetlands, fooding some lands adjacent to the current

    mangrove area (Figs. 1, 2, 5 and 6). The small estuary

    zone o Ventanas Beach will be signicantly inundated,

    making the road parallel to the beach and the buildings

    in this sector highly vulnerable (Figs. 7 and 10).

    A quantitative assessment o the current tectonic ten-

    dency in the area is still pending, in order to estimate

    the component o sea-level rise due to the subsidence

    o the continental platorm. The west coast o the Nicoya

    peninsula, on which Playa Grande is located, is subsid-

    ing. Observations in Junquillal beach suggest, that in

    act, the mean sea level is rising along this stretch o

    the coast. It is evident that the ocial landmarks o the

    public zone need to be relocated inland, since their dis-

    tance to the ordinary high tide line is noticeably less

    than 50 meters. The tendency o the relative sea level

    in Puntarenas or the period 1941-1978 is a net rise,

    with a total increment o 51 mm over that period . The

    current high tide level (usually drawn and dened as the

    boundary between the maritime and terrestrial domains

    or cartographic and legal purposes) is inundated ap-

    proximately 8% o the time. However, i average sea

    level rises by 1 m, this value increases to 51%, which is

    the percentage o inundated time currently correspond-

    ing to the mean tide level (mean between the average

    low and the average high tide). Unortunately, there is

    lack o data series or changes in sea level along the

    Pacic littoral o Costa Rica, which have the continuity

    and duration needed to estimate with more precision

    these tendencies or several locations along the coast(A. Gutirrez, personal communication).

    Sea level rise is a gradual process. Extreme tidal action

    will increasingly reach those areas that today seem sae

    rom inundation. Along the northern Pacic coast o Cos-

    10 Fish, M.R., I.M. Cote, J.A. Gill, A.P. Jones, S.

    Rensho and A.R. Watkinson. 2005. Predicting the

    impact o sea-level rise on Caribbean sea turtle nest-

    ing habitat. Conservation Biology 19:482-91.

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    Figure 1. Inclined orthophotograph o Playa Grande

    illustrating the inundation area corresponding to a 1-meter

    sea level rise, probable by the end o the century.

    Figure 2.DTM image o Playa Grande topographyillustrating dierences in elevation details in relie with

    15-cm vertical resolution and the inundation area

    corresponding to 50-cm and 100-cm sea level rises.

    Conclusion

    Flooding models are needed or dierent sea level rise

    scenarios in order to better plan or coastal develop-

    ment, in a way that would benet both sea turtles and

    local residents. This project aims to contribute case

    studies to enhance knowledge o the coastal process-

    es associated with climate change on beaches o the

    tropical Eastern Pacic that will allow better manage-

    ment o the challenges o erosion, territorial manage-ment, conservation o marine-coastal biodiversity and

    responsible development. The uture o Playa Grande

    beach depends on its capacity to retreat rom rising

    sea levels while maintaining ideal ecological condi-

    tions or leatherback nesting. This implies that existing

    and uture inrastructure must not block this retreat

    and that the buer zone o the national park ensures

    eective environmental mitigation measures or the

    uture landward location o the beach. Due to the ore-

    cast retreat o the beach, a rectication o the park

    boundaries that would reduce its current width and

    allow continued development o inrastructure withinthe 125-meter strip above the current regular high

    tide level is neither a precautionary nor a preventa-

    tive measure and it would compromise in the medium

    and long term its ecological unction as a leatherbac

    nesting site, the very reason or which this protected

    area was declared. The implementation o adaptatio

    measures or climate change on nesting beaches is

    an international commitment under the Inter-Ameri

    can Convention or the Protection and Conservation o

    Sea Turtles, to which Costa Rica is a signatory party

    In implementing such measures, Costa Rica has the

    opportunity to maintain its regional leadership in seaturtle conservation and as a global reerence in biodi

    versity conservation.

    Figures

    Year 2009

    Year 2009 + 50 cm + 100 cm

    + 100 cm

    Source:WWF/Stereocarto

    So

    urce:WWF/Stereocarto

    Source: WWF / Stereocarto

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    Figure 3. Inclined orthophotograph o Playa Grande, taken

    on June 6, 2009.

    Figure 4. DTM image o Playa Grande topography

    illustrating details o dierences in elevation in relie with

    15-cm vertical resolution. Note the low elevation o the

    mangrove zone around the Tamarindo estuary and the

    estuary behind Ventanas Beach. The beach dune stands

    out with an elevation a little higher than the landward

    terrain behind it.

    Source:WWF/Stereocarto

    Source:W

    WF/Stereocarto

    Actual sea level

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    Figure 5. Comparison o vertical image orthophotographs o the eastern sector o Playa Grande illustrating current

    sea level (above) and the inundation area with a 100-cm sea level rise, estimated or the end o the century. This

    image does not include the expected 50-m displacement o the beach landward (see Fig. 9).

    Source:WWF/

    Stereocarto

    Source:WWF/Stereocarto

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    Figure 7. Comparison o vertical image orthophotographs o Ventanas Beach, western sector o Playa Grande, illustrating current sea level (above) and the inundation area

    with a 100-cm sea level rise, estimated or the end o the century (below). This image does not include the expected 50-m displacement o the beach landward (see Fig. 10).

    Source:WWF/Stereocarto

    Source:WWF/Stereocarto

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    Figure 8. Comparison o vertical orthophotographs o Playa Grande illustrating current sea level (above) and a 100-cm sea level rise, estimated or the end o the

    century (below). This image recreates the expected 50-m displacement o the beach landward in response to sea level rise. Some buildings would end up on the

    beach, subject to the impact o storm surges. Note that the road parallel to Ventanas Beach is highly vulnerable to eventual erosion, as it is situated on a narrow

    sand bank, lanked by water on both sides and exposed to the beating o the waves and storm surges (let side o the image).

    Source:WWF/Stereocarto

    Source:WWF/Ste

    reocarto

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    Figure 9. Vertical orthophotograph o Playa Grande, illustrating areas o Las Baulas National Park in this sector, as well as the expected landward

    displacement zone o the beach o 50 m in response to sea level rise, estimated using the Bruun rule (see the text).

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    Figure 10. Vertical orthophotograph o Playa Grande and Ventanas Beach, illustrating areas o Las Baulas National Park in the northwestern sector, as

    well as the expected landward displacement zone o the beach o 50 m in response to sea level rise, estimated using the Bruun rule (see the text).

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