THE DEVELOPMENT OF STRATEGIES TO MAINTAIN AND ENHANCE THE - - PowerPoint PPT Presentation

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THE DEVELOPMENT OF STRATEGIES TO MAINTAIN AND ENHANCE THE - - PowerPoint PPT Presentation

The Biodiversity Resource Mobilisation (ResMob) project of the Ministry of Environment and Tourism (MET), in partnership with GiZ TEEB COUNTRY STUDY: THE DEVELOPMENT OF STRATEGIES TO MAINTAIN AND ENHANCE THE PROTECTION OF ECOSYSTEM SERVICES IN


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Namibia TEEB study

The Biodiversity Resource Mobilisation (ResMob) project of the Ministry of Environment and Tourism (MET), in partnership with GiZ

TEEB COUNTRY STUDY:

THE DEVELOPMENT OF STRATEGIES TO MAINTAIN AND ENHANCE THE PROTECTION OF ECOSYSTEM SERVICES IN NAMIBIA’S STATE, COMMUNAL AND FREEHOLD LANDS

June 2017 Anchor Environmental Consultants & Namibia Nature Foundation

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Study objectives

  • Support ResMob project in conducting

main study phase of TEEB country study:

– Economic valuation of ecosystem services – Contribution of these ecosystem services to national priority sectors – Costs of their overuse and depletion through economic activities

  • Inform the resource mobilisation strategy
  • n economic and policy instruments
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A NATIO TIONAL A ASSESS SSESSME MENT O OF NAMIB MIBIA’S EC S ECOSY SYST STEM SERV SERVICES

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Provision of harvested resources

  • Used sustainable yields of

services, and modified based on demand (where possible).

– Woody resources – Non-woody raw materials – Wild foods & medicines – Inland fisheries

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  • Based on replacement

cost of fodder for livestock.

  • Used livestock numbers, %

body weight consumption

  • Value given in areas

where livestock density<carrying capacity,

  • therwise only carrying

capacity valued.

  • Distribution of value

– 60% Freehold land – 40 % Communal land

Fodder provision

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Game

  • Value of sustainable off take

for meat production and trophies based on regional population estimates or game counts in conservancies with hunting partner

  • Only for large game species

(not antelope smaller than springbok)

  • Value concentrated in freehold

land where game population have higher densities.

  • Possible overestimate as

demand is unknown.

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Tourism value

  • Total tourism expenditure in

Namibia is N$16.4 bn

  • Leisure tourism expenditure is

N$13.1 bn

– We mapped this based on densities

  • f georeferenced photos on Flikr

– Parks – 42% – Communal conservancies – 35% – Freehold rangelands – 23%

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Carbon storage

  • Based on biomass carbon

in vegetation.

  • Values based on the global

social cost of carbon, scaled to Namibia based on GDP and vulnerability to climate change index.

  • N$38 million of damages

costs avoided to Namibia and N$2153 billion globally.

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Hydrological services

  • Groundwater recharge

– N$538 million/yr

  • Flood attenuation
  • Sediment retention
  • Water quality

amelioration

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Other support services

  • Agricultural

– Pollination, pest control

  • Fisheries

– Critical breeding and nursery grounds

  • Hunting and wildlife

tourism

– Critical seasonal refugia, breeding areas

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WP1 WP1: STA : STATE TE PROTEC TECTED TED AR AREAS AS

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Namibia’s protected area network

  • Approximately 17% of Namibia

is formally protected

  • Core strategy for biodiversity

conservation (NBSAP2)

  • Contributes significant value

to the national economy

  • Avg. 9% annual increase in

tourist arrivals 1995-2015

  • In 2008, PA-tourism generated

2.1% direct value added GDP, 3.8% total value added

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Main threats to maintaining biodiversity and ecosystem values

  • Proximate threats

– Poaching – Overstocking (artificial waterholes) – Excessive disturbance and off-road driving by tourists – Mining – Climate change

  • Systemic challenges

– Lack of financial resources – Lack of capacity – Persistent poverty outside PAs

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Park financing system

  • Protected areas continue to experience substantial

underfunding

  • Three main sources of funding for PAN: government,

donor & park revenues channelled via GPTF

  • Park revenues go

directly to central government with

  • nly a portion of

these revenues being reinvested into the management of national parks

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Park financing gap

  • Funding for protected area management is

currently in the order of N$215 million

– Represents 48% of MET budget

  • Estimated annual recurrent expenditure of

N$275 million required for park management

– Shortfall of about N$60 million

Source: MTEF 2016/17-2018/19 Updated from Turpie et al. (2010)

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Park fees & revenues

  • Park fees same for all larger parks, lower for smaller

parks & heritage sites

  • Park fees have remained unchanged since 2005

– Parks have become cheaper for most users – Potential foregone income is significant (70% of visitors to larger parks are int. or regional tourists)

  • Park fees generated N$56.4m in 2014/15
  • 90% of revenues collected by DWNP
  • 26% of DWNP expenditure

Daily entrance fee (2017 N$) Park Citizen SADC International Etosha, /Ai-/Ais Hot Springs, Skeleton Coast, Namib-Naukluft, Waterberg Plateau

30 60 80

All other parks, reserves and heritage sites

10 30 40

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Regional comparison

  • Current prices for PA’s in Namibia are low

– Lowest prices in the region – International visitor park fees in Namibia are half those charged in Botswana, a third of those in Zim, RSA & Zambia and a tenth of the price charged in Kenya and Tanzania

2 2 5 5 2 7 4 5 13 12 10 15 10 32 6 13 16 19 20 56 64

20 40 60 80

Namibia Botswana Zimbabwe South Africa Zambia Kenya Tanzania

Fee pppd (US$)

Local Regional (SADC/EAC) International

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Recommendations

Namibia needs to update its tariffs and address other institutional issues influencing the efficiency of park revenue systems: 1. Change the institutional set-up

– DWNP as parastatal and/or parks under long-term contractual agreement with an organisation like African Parks – NWR resorts should be sold to private operators

2. Determine optimal prices

– Significant opportunities for increasing current tariffs – Understand local and international demand, PA objectives

3. Improve revenue collection and management

– More secure fee collection systems – PA revenues entirely retained by the managing authority

4. Expand revenue collection to accommodation facilities

– Resorts within the parks should pay rental and royalties to Parks

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WP2: C WP2: COMMU MMUNAL CONSERVAN RVANCIE IES

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CBNRM

Source: NACSO 2015

  • 1993 - MET established CBNRM support structure
  • 1996 - legislation allowed local communities to

create conservancies and enter into arrangements with private companies

– Royalty payments & direct income provide incentive

  • 82 conservancies established in 20 years
  • Now cover 20% of Namibia (165 182 km2)
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Conservation outcome

  • General increase in

wildlife numbers across the country from 1982-2000, then stabilised

  • Drought since 2012

has reduced wildlife numbers in some areas

Total population Number of animals/km

Source: NACSO 2015

North West Zambezi Region

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Development outcome

  • Recognised as a national

development strategy

  • Allows diversification,

additional income

  • pportunities
  • Generated N$102 million

for local communities in 2015

– $0-$7.2m per conservancy

  • Created 5116 jobs in

2015

Concessions Community forests Emerging conservancy Registered conservancy

Source: NACSO 2015

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Challenges

  • Not all conservancies add the value that they could

– Institutional problems – Variation in potential, newer ones struggle – Household members drinking the proceeds

  • Conservation people claim that wildlife is declining

– Petty poaching and human encroachment – Organised poaching and wildlife crime

  • Conservancy members claim that wildlife is

increasing too much

– Human-wildlife conflict

  • Problems exacerbated by drought

– Fewer antelope, lower meat distribution – Increased HWC (hungry predators, thirsty elephants) – Increased poaching

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Some hypotheses/thoughts

  • Conservancies establishment has happened at relatively

low cost to local inhabitants

– i.e. people have largely carried on with whatever they were doing, minor sacrifices if any – HWC problems have not increased on average

  • Refraining from damaging activities is more likely to be as

a result of increased control/sanctions rather than co-

  • peration to benefit from increased JV income, except

where JV income is high

  • Stochastic delivery of benefits (e.g. wildlife meat offtake)

is having a perverse impact on household co-operation

  • Increasing wildlife protection will decrease stock

depredation but increase elephant damage

  • The relative damage by individual local households vs
  • rganised poachers needs to be assessed
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What scope is there for PES?

  • JV arrangement already provides ‘incentive’
  • Steady income, % of turnover is indirectly linked to wildlife
  • Has had high but variable level of success
  • but still much opportunity for improvement
  • The more the better
  • Increased income would help to solve both institutional

problems and household co-operation

  • We have only scratched the tip of the iceberg
  • Benefits currently come directly from JV businesses
  • Plenty of scope to channel income from other beneficiaries -

tourists, Namibians (GN), Rest of World (Donors)

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Communal conservancy Ecosystem services

Locals All Nami bians Value of natural systems Locals Namibians Rest of world Provision of harvested resources Local value

  • Agricultural and fishery

support services Local value

  • Refugia
  • Significant to

surrounding conservation areas Groundwater recharge Local value Value in longer term

  • Wildlife & unspoilt

landscapes N$102 million - damages N$1.8bn + national WTP Visitors’ consumer surplus + global WTP Carbon storage N$3.8m N$18.9m N$1071bn Options for PES

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What could PES achieve

  • Aim would be to discourage encroachment into areas

set aside for wildlife, burning and excessive harvesting/hunting (poaching).

  • PES as a direct payment to households may not

achieve desired effect due to tragedy of the commons (free-riding)

  • However could be effective if a substantial portion is

invested in conservation measures

  • PES (or any incentive measure) cannot be expected to

address high-value, organised wildlife crime

– This has to be addressed by Gov (PA?) – This is increasingly going to be a prerequisite for the success of other measures

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Payments for Ecosystem Services

  • Beneficiaries pay land
  • wners/managers for

delivery of a service such as water, carbon or biodiversity

  • Seller will have to incur

some costs to provide the ecosystem service

  • The payment

compensates the landowner for these costs

  • The payment is

conditional on delivery

Benefits to locals Costs to rest of society

Without PES With PES

Agric & NR income Water/ carbon losses PES Agric & NR income

e.g. paying to reduce deforestation

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PES for conservancies

HH share

Cons

Liveli- hood income Costs

JV income and allocation Household income

Residual HWC

HWC

HH share Income HH share

Cons

Liveli- hood income Costs

JV + PES income and allocation Household income HWC

Income HH share

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Proposed design

  • Build on existing structures

– additional to existing JV arrangement – payment to existing structure, but with external treasurer from NGO

  • Funding from donors and tourist

voluntary contributions

– to central managed endowment fund

  • Payment is linked to wildlife status

– Annual habitat assessment + census – Status takes climate conditions into account

  • Simple computational system for

determining reward level

– E.g. $1*HaOK+$2*HaGood+$3*HaExcellent

  • Pooled income is split between

conservation management + households

– Payments spread e.g. quarterly – Meat (any type) as well as cash

  • Continued capacity-building support will

be necessary

Wildlife status Wildlife counts

Habitat assessment

Scoring system Conservation action Community and hh benefits PES Payout Existing conservancy income Conservancy funds Payment rules

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Proposed study area

  • 3 conservancies in Southern

Kunene region.

  • 1. Uibasen-Twyfelfontein: (1999)

100% of income from JV tourism, home to Twyfelfontein World Heritage Site, well managed.

  • 2. Sorris-Sorris: (2001) JV

tourism 65%, hunting 13% of income, institutional problems & some misappropriation of funds.

  • 3. Tsiseb: (2001), JV tourism 99%

& hunting 1% of income, home to Brandberg Mountain & White Lady rock paintings, some institutional problems.

Arid landscape, <100 mm annual rainfall

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Field experiments & surveys

  • Aims:

– To establish likelihood of co-operation in a system where rewards are introduced – To determine how reward levels, baseline income and institutional effectiveness affect co-

  • peration
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Proposed approach

  • Behavioural experiments

– ~180 participants from 3 conservancies – a game played in groups, with varying treatments.

  • The game

– Members of each group are given a sum of real money, representing the current benefits received by households. – PES system is explained.

  • The more invested, the more difficult it will be for people to

infringe on conservation rules

  • The payoff depends on total group investment.
  • The more invested, the greater the payoff.

– Members have to decide how much to invest in conservation action. – Several rounds are played, and a $ payout is given to players.

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Proposed approach

  • Brief participant survey after the game

– Gender, age, education – Main sources of income – Benefits received from conservancy last year – HWC damages experienced last year – Extent to which increased surveillance would impact own hh livelihood – Confidence in conservancy management

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Next steps

  • Finalising of experiment details & logistics
  • Fieldwork in mid-July

– Training of field co-ordinators – 2-3 days in each conservancy

  • Analysis in August
  • Write-up in Sep/Oct
  • Research results
  • Recommended set-up for Namibian conservancies
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Outputs

  • Average contributions to

conservation at different levels

  • f the PES (low, medium, high)
  • Untangle how institutional

elements (such as mismanagement) and other key metrics (other livelihood sources, age) impact on contributions

  • This informs the design of the
  • PES. For example, if trust in

management impacts on cooperation, the PES will need to be externally audited

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Design

  • Option 1: Vary the PES

– Vary the level of the PES (low, middle and high PES) – This gives an indication of when cooperation rates shift under the different PES levels – Capture metrics such as mismanagement through the survey (relevant for option 2) – Capture information on benefits received over the past year through the survey (relevant for option 3)

  • Option 2: Vary the level of external oversight

– Test one level of PES but vary the framing around the level of external oversight – Only in one treatment is the involvement of an external auditor explicitly mentioned – The results would give an indication of the degree to which concerns around management inhibit cooperation

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Design

  • Option 3: Vary the level of endowment

– Within each treatment, have high-endowment and low- endowment groups – The endowment acts as a proxy for JV income (high- endowment groups have a relatively higher JV income) – The results would indicate how cooperation varies across the income levels

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Thank you! Any queries/suggestions/information to: jane@anchorenvironmental.co.za