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Conservation challenges at Peninsula

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Photo: O. Sakharov Conservation challenges at Fildes Peninsula HansUlrich Peter 1 , Jan Esefeld 1 , Fritz Hertel 2 , Osama Mustafa 3 , Simone Pfeiffer 4 , Christina Braun 1 1 Polar & Bird Ecology Group, Institute of Ecology, University of Jena, Germany 2 Federal Environment Agency, DessauRosslau, Germany 3 ThINK Thuringian Institute for Sustainability and Climate Protection, Jena, Germany 4 Section for Tropical and Subtropical Agriculture and Forestry, University of Goettingen, Germany
Transcript

Phot

o: O

. Sak

haro

v

Conservation challengesat Fildes Peninsula

Hans‐Ulrich Peter1, Jan Esefeld1, Fritz Hertel2, Osama Mustafa3, Simone Pfeiffer4,Christina Braun1

1 Polar & Bird Ecology Group, Institute of Ecology, University of Jena, Germany2 Federal Environment Agency, Dessau‐Rosslau, Germany

3 ThINK Thuringian Institute for Sustainability and Climate Protection, Jena, Germany4 Section for Tropical and Subtropical Agriculture and Forestry, University of Goettingen, Germany

IntroductionStudy area

• Southwestern part of King George Island• Intensively used for scientific, logistic and

tourism‐related activities

Introduction

Fildes Peninsula‐ King George Island ‐

58 58‘ W, 62 12‘ SProjection & Coordinates:

UTM (Zone 21 E)

Dart Island

Two Summit Island

Ardley Island

Nebles Point

Marsh (CHL)

Ripamonti Base (CHL)Ballve (ARG)

Ripamonti Refuge (CHL)

Great Wall (CHN)

Priroda (RUS)

Artigas (URU)

Bellingshausen (RUS)

Frei (CHL)

Escudero (CHL) Estación Marítima Antárctica (CHL)

Nation Station name Open sinceChile Estación Marítima

Antárctica1987

year‐round since 2005

Chile Escudero 1994

Chile Frei & Marsh 1969

China Great Wall 1985

Russia Bellingshausen 1968

Uruguay Artigas 1984

Source: COMNAP Antarctic Facilities List 2014, Antarctic Treaty Electronic Information Exchange System

Study area

• Populated since 1968• Six stations, several field huts• Runway turns the area into a 

logistic hub for inter and intra‐continental flighs

• Western Maxwell Bay asgateway for ships and yachts

Adelie Penguin 307 ‐ 559 ↓

Chinstrap Penguin 8 ‐ 29 

(~ 70 Drake coast)

Gentoo Penguin 4429 ‐ 6417 ↑

South. Giant Petrel 225 ‐ 407 ± 0

Light‐mantled Sooty Albatross 0 ‐ 5 ± 0

Cape Petrel ≈ 70 ‐ 450

Wilson’s Storm Petrel ~ 3500 ‐ 5000 ± 0

Blackbellied Storm Petrel ~ 500 ‐1000 ± 0

Lesser Sheathbill 1 ‐ 2 ± 0

Brown Skua 27 ‐ 85 ± 0

South Polar Skua 12 ‐ 254 ↑

Mixed / Hybrid Skua Pairs 2‐32 / 0 ‐ 24 ± 0

Kelp Gull 50 ‐ 139 ± 0

Antarctic Tern <100 ‐ 900 ↓

Breeding pair number of birds and their trends(seasons 2003/04-2005/06 & 2008/09-2013/14)

ResultsBreeding birds

Breeding site of four seal species andthirteen bird species

Introduction

2 Antarctic Specially Protected Areas

Study area

No. 150 Ardley Island

No. 125 Fildes Peninsula: 

rich fossil deposits

high species diversity of 

fauna & flora

Introduction

4 Historic Sites and Monuments (HSM) commemorating historic events

Large concentration of historical/archaeological sites dating from the 1820s

Study area

IntroductionConflict of interests

Fildes paradigm

OutlineData collection

b) Assessment of the current impact of station logistic, scientific activities, leisure        activities of station members to certain indicator species (fauna and flora)

a) Survey of numbers and distribution of flora and fauna

c) Assessment of the current environmental impact of tourist activities to certain  indicator species (fauna and flora)

e) Evaluation of current and expected environmental risks (e.g. by cumulative effects or non‐native species) 

d) Assessment of the current environmental impact of tourist activities to certain  indicator species (fauna and flora)

• Human impact research since 2003/04: risk assessment

• Recent research to provide an update of dataset and to point out new developmentsc

Season

1970 1975 1980 1985 1990 1995 2000 2005 2010 2015

Bree

ding

pai

r num

ber

Gen

too-

& A

délie

pen

guin

s

0

2000

4000

6000

Chi

nstra

p pe

ngui

ns

0

50

100

150

200

Adélie penguin (P. adeliae)Chinstrap penguin (P. antarctica)Gentoo penguin (P. papua)

species population trend1979/80 – 2013/14

mean breeding success (20 years)

Adélie penguin ‐ 92% 1,20 ± 0,21

Chinstrap penguin ‐ 44 % 1,17 ± 0,37

Gentoo penguin + 73 % 1,28 ± 0,22

Penguin populationBreeding birds

Significant trends in breeding pair numbers of three sympatric Pygoscelid penguins

Southern giant petrel (SGP) = highly sensitive to noise and disturbance

Giant petrel populationBreeding birds

monitoring data since 1979/80stable population

but

striking variations betweenvarious sub‐colonies

South

East

North

South‐east

SGP breeding sites (pooled into 4 groups) showed clear response to construction of new station in the 1980s through nest site shift.

Giant petrel populationBreeding birds

Season

1980

1985

1990

1995

2000

2005

2010

2015

Bre

edin

g pa

ir nu

mbe

r

0

50

100

150

200

Season

1980

1985

1990

1995

2000

2005

2010

2015

Bree

ding

pai

r num

ber

0

50

100

150

200

Season

1980

1985

1990

1995

2000

2005

2010

2015

Bre

edin

g pa

ir nu

mbe

r

0

50

100

150

200

Season

1980

1985

1990

1995

2000

2005

2010

2015

Bred

ing

pair

num

ber

0

50

100

150

200

East

• New changes in breeding pair numbers in the last decade

• Significant decrease of giant petrel breeding success since 1979/80

• Changes not attributable solely to environmental conditions as adjacent sub‐colonies were unequally affected

• Areas frequently visited  during summer by station members showed greater declines

• Slight increase in non‐visited areas  nest site shift

Giant petrel populationBreeding birds

Season1980 1990 2000 2010

Chi

cks/

Pai

r (%

)

0

10

20

30

40

50

60

70

R2 = 0.38, p = 0,01

SGP as indicator of human disturbance

ResultsSea traffic

• Strong increase of ship arrivals (mean: 77 ship arrivals per season, max.: 102)

• On average ship activity on 75 % of days of the study period

• Increasing proportion of cruise vessels offering air‐cruise programs

Season

2003/04

2004/05

2005/06

2006/07

2007/08

2008/09

2009/102010/112011/122012/132013/14

Num

ber o

f shi

p ar

rival

s

20

40

60

80

100

120

140

Proportion of ship days (%)

20

40

60

80

100

MiscellaneousPatrol vesselSupply vesselResearch vesselCruise vesselYacht Ship days (%)

study period:10 December – 26 February = 79 daysno data for 2006/07 & 2007/08

ResultsSea traffic

• Intensive ship and yacht traffic lead to various risks for the environment and human safety

• Example = sinking of a private yacht in April 2012 (risk of an oil spill in a sensitive area) and yacht recovery in January 2013 (huge logistic and manpower effort).

Foto: R. Eliseev

Foto: R. Eliseev

ResultsSea traffic

• on average on 62 % of ship days with more than one ship per day (max.: 85 %)• often connected with flight activity

Cumulative effects

Season

2003

/0420

04/05

2005

/0620

06/07

2007

/0820

08/09

2009

/1020

10/11

2011

/1220

12/13

2013

/14

Freq

uenc

y in

day

s

0

10

20

30

401 Ship per day 2 Ships per day 3 Ships per day 4 Ships per day 5 Ships per day 6 Ships per day 7 Ships per day

study period:10 December – 26 February = 79 daysno data for 2006/07 & 2007/08

Increasing accumulation of ship activities(mainly logistic operations and passenger transfers)

Crabeater seal injured by Zodiac propeller

ResultsAir traffic

• In total no increase in number of days with aircraft activity (mean 68 % days of the study period )

• Helicopter ↓, Hercules C‐130 ↑, private company DAP ↑

Season

2003

/0420

04/05

2005

/0620

06/07

2007

/0820

08/09

2009

/1020

10/11

2011

/1220

12/13

2013

/14

Day

s w

ith a

ircra

ft ac

tivity

0

20

40

60

80

100

120

HelicopterSmaller airplanes *Hercules C-130Passenger Jet (Boeing, Airbus)

study period:10 December – 26 February = 79 daysno data for 2006/07 & 2007/08

ResultsAir traffic

study period:10 December – 26 February = 79 daysno data for 2006/07 & 2007/08

• on average on 67 % of aircraft days with more than one aircraft operation per day

• often connected with ship activity (tourist transfer)Cumulative effects

Season

2003

/0420

04/05

2005

/0620

06/07

2007

/0820

08/09

2009

/1020

10/11

2011

/1220

12/13

2013

/14

Num

ber o

f day

s

0

5

10

15

20

25

1 Aircraft per day2 Aircrafts per day3 Aircrafts per day4 Aircrafts per day 5 Aircrafts per day6 Aircrafts per day7 Aircrafts per day8 Aircrafts per day

Increasing accumulation of aircraft activities)

Resolution 2 (2004) XXVII ATCM:Guidelines for Aircraft near concentrations of birds:  minimum vertical distance: ~ 610 m above bird coloniesminimum horizontal distance: 200 ft (~ 610 m) from bird colonies, 1/4 nautical mile (~ 460 m)from the coastline 

season 2004/05

ASPA No. 150

ResultsAir traffic near Ardley Island

Low overflights over Ardley Island were common in the past.

Penguin colony

Hercules C‐130

ResultsAir traffic near Ardley Island

* Twin Otter, Beechcraft King Air A‐100, Dash‐7,BAE 146, Basler BT‐67, DC‐3, etc.

Season

2003

/0420

04/05

2005

/0620

06/07

2007

/0820

08/09

2009

/1020

10/11

2011

/1220

12/13

2013

/14Num

ber o

f Ard

ley

over

fligh

ts/a

ppro

ache

s

0

20

40

60

80Helicopter Smaller airplanes *Hercules C-130

• Significant reduction of aircraft use near Ardley Island (ASPA No. 150: penguin & southern giant petrel colonies)

• Suspected reason: increased acceptance and implementation of the guidelines

study period:10 December – 26 February = 79 daysno data for 2006/07 & 2007/08

Oil contaminationrecent oil spill (station’s fuel pipeline & tank), elution of contaminated soil, 

vehicle leakages

Oil contamination & Waste management Results

Waste management

Observed shortcomings:  ‐ Open waste deposits & Open waste burning‐ Land fill of waste‐ Active feeding of birds‐ Open discharge of organic waste

Decay of building and research installationsEnduring distribution of waste

ResultsStation extensions

Great Wall Station

Stations Frei, Escudero, Est. Marítima

Bellingshausen Station

Artigas Station

Station extensions in the last decade lead to an increased number of station members≈ 120 in winter (+ 30 %)> 300 in summer (+25 %)

ResultsConstruction activities

Negative environmental impacts, mainly caused by the extractionof construction material.

• Damage of beach ridges of high scientific value

• Damage of vegetation 

• Damage of breeding grounds of seabirds

• Disturbance of resting seals

Increase of vehicle use beyond the existing road net (esp. by Quads bikes) causing vegetation damage and disturbance of birds

ResultsHuman activities

Leisure activities of station members

excursions into sensitive areas (fishing, barbecue)“sunday visits” to Ardley Island (ASPA No. 150)

ResultsHuman activities

Not in compliance with ASPA Management Plan (Ardley Island)crossing areas with dense vegetation, bird breeding sites (skuas, terns)disturbance of animals (e.g. chasing, touching, catching)

Results

Alarming lack of knowledge of code of conducts andlegally binding regulations like the ASPA Management Plans!

Human activities

Wide range of tourism and other activities, still expanding!sea‐borne tourism (only station visits or short guided walks) air‐borne tourism (guided walks)air‐sea‐borne tourism (cruise ship passenger exchange)adrenalin sport activities (basejumping, kiting, surfing)Manager Training Wharton University, Pennsylvania, USA (guided walks, camping)Marathon (4 events scheduled for 2014/15)educational programsmedia teamsgovernmental delegationsprivate use of Unmanned Aerial Vehicles (UAV)

Conclusions

• Notable improvements:− reduction of very low overflights over protected or sensitive areas− waste collection and removal− installation of up‐to‐date sewage treatment plants

• Still existing environmental shortcomings:− waste management (dumping of organic material, open waste deposits, open waste burning, land fill)

− fuel and oil handling− insufficient reaction after a larger oil spill− vehicle traffic beyond the road net  vegetation damage−material extraction for construction activities  damage of vegetation, bird breeding sites and beach ridges

− leisure activities affecting breeding birds, seals and vegetation− lack of knowledge of station members regarding existing guidelines to protectfauna and flora (even of ASPA Management Plans)

− tourists without guidance and knowledge about existing regulations− relatively low scientific and logistic co‐operation and coordination

Human activities

If no additional management measures will be applied, the expected environmental risk will probably increase further.

ConclusionsManagement

Fauna index Visitor indexConflict potential

Zoning recommended as a visitor management tool

Overlay of seabird monitoring data and visitor observations to detect conflict zones

Boundary corners62 14 26 S ‐ 62 08 16 S58 50 36 W ‐ 59 02 45 W

Area62.5 km2

Proposal by Germany (2007):Antarctic Specially Managed AreaFildes Peninsula Region

Boundary of 1/4 nautical mile (~ 460 m) from the coastline according to the recommendation ofWorking Paper on Guidelines for the Operation of Aircraft near Concentrations of Birds in AntarcticaXXVII ATCM, Cape Town, 2004

ConclusionsManagement

CEP: International Working Groupabout Possibilities for Environmental Management of Fildes Peninsula Region

Convenors: Germany, Chile

Revised Management PlanASMA Fildes Peninsula Region: ATCM XXXIII WP 40 Annex II

Proposals:‐ Designation of ASMA FildesPeninsula Region‐ Implementation of spatialzoning system

ConclusionsManagement

No agreement upon anyimproved management

• Implementation of a general Fildes Peninsula Region Code of Coduct,suppl. by C. o. C. for Facility Zones, C. o. C. for Scientific Research and C. o. C. for Visitors

• Establishment of a Management Group− implementation of management guidelines− coordination of ASPA visits− organization of meetings

• National Antarctic Programs ensure briefing of station personnel about the requirementsof the Management Plan and supplemental documents

• Tour operators ensure briefing of visitors about the requirements of theManagement Plan and supplemental documents

• Harmonization/ improvement of contingency plans for station emergencies,oil spills, etc. recommended

Further possible activities to improve area protection and management :

Management Conclusions

Acknowledgements:

• J. Krietsch, U. Grünewald, T. Guetter, T. Herrmann, T. Kahl, S. Janowski, A. Nordt, A. Nordt, M.C.-Rümmler, M. Stelter

• all members of the Fildes stations

Foto: Sakharov

Thank you for your attention!

Peter, H.‐U., Buesser, C., Mustafa, O. & Pfeiffer, S. (2008): Risk assessment for the Fildes Peninsula and Ardley Island, anddevelopment of management plans for their designation as Specially Protected or Specially Managed Areas:(http://www.umweltbundesamt.de/sites/default/files/medien/publikation/long/3478.pdf)

Braun, C., Mustafa, O., et al. (2012): Environmental Monitoring and Management Proposals for the Fildes Region (KingGeorge Island, Antarctica). Polar Research 31, 18206.

Braun, C. & Lüdecke, C. (2012): Fildes Peninsula – A Place of Threatened Historic Sites. Presented at: IPHC Conference"Conservation Challenges, Solutions and Collaboration Opportunities in Uncontrolled Environments", Hobart,International Polar Heritage Committee:http://www.polarheritage.com/content/library/Cornelia_Luedecke_Brau_IPHC_2012.pdf.

Peter, H.‐U., Braun, C., Janowski, S., Nordt, A., Nordt, A., Stelter, M. (2013): The current environmental situation andproposals for the management of the Fildes Peninsula Region:http://www.umweltbundesamt.de/sites/default/files/medien/461/publikationen/4424.pdf


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