Paul Jepson, Made Sri Prana, Sujatnika and Fahrul Amama
TRAFFIC Bulletin Vol. 22 No. 1 (2008)
Introduction
The hugely popular Indonesian pastime of keeping wild birds for pets is threatening the long-term survival of many songbird species on the islands of Java and Bali (BirdLife International, 2001; Jepson and Ladle, 2006). In response to this threat, the authors have been working with leaders of the songbird-keeping fraternity to develop a non State, market-based governance approach to guide consumer preferences in Indonesia away from wild-caught birds towards captive-bred alternatives. A key component of this approach is empowering consumer choice through the establishment of a labelling system to certify bird-breeding facilities in Indonesia.This paper reports on the development and initial design of the certification tool. The broader approach to governing includes planned activities to: i) market captive-bred birds as more desirable on ethical and quality grounds; ii) increase the supply of captive-bred birds; iii) a social marketing campaign to encourage ethical and sustainable bird purchasing choices (and dissuade casual purchase of birds); and, iv) promote the prestige of captive-bred ‘ring class’(classes of birds that are captive bird and hence ringed) birds at songbird competitions.
The authors' design of this system of governing is informed by a research project that comprised two phases: 1) a questionnaire survey and media analysis to generate overview data on the scale and attributes of bird-keeping and scope out the key actors, networks and motivations? that need to be influenced, and 2) in-depth interviews and workshops that aimed to reveal insights on the contemporary culture of bird keeping in Indonesia and identify and engage influential actors within the bird-keeper fraternity in the development of A a suitable and effective policy approach.
Bird-keeping and breeding in Java and Bali
Bird keeping is hugely popular in Java and Bali.In the six cities surveyed during April 2006, 35.7% (636 out of 1781 households surveyed) of households kept a bird and 57.6% had kept a bird in the last 10 years.A projected 1.45 million households keepan estimated 2.15 million wild-caught birds (Jepson and Ladle, in press).
Entering songbirds into competitions is a popular recreation in Java and Bali (and now gaining popularity in Kalimantan and Sumatra). Five of the nine species regularly found in competition are among the ten commonest species kept, namely Canary Serinus canarius, Long-tailed Shrike Lanius schach, Orange-headed Thrush Zoothera citrina, White-rumped Shama Copsychus malabaricus, and Magpie Robin Copsychus saularis (Jepson, 2008)
Preliminary projections arising from the survey suggest that songbird keepers contribute approximately €50 million to the economy of these six cities. Of this, ca €31.6 million is produced by the sale and trading of birds, ca €7.5 million from the collection, breeding and sale of live food (ants eggs, worms, crickets) and ca €5.6 million from the manufacture and selling of bird cages. This figure does not include other aspects of the hobby which may make significant economic and employment contributions, namely bird markets, song contests and bird-breeding enterprises (Jepson, Ladle and Sujatnika, in prep).
Species such as Canary, Zebra Dove Geopelia striata and lovebirds Agapornis are bred in large numbers. The rise in popularity of songbird keeping since the mid-1990s, combined with declining wild populations, is resulting in a growth in the number of songbird breeders. Breeders now produce species such as Straw-headed Bulbul Pycnonotus zeylanicus, White-rumped Shama, Chestnut-capped Thrush Zoothera interpres, Asian Pied Starling Sturnus contra, Bali Starling Leucopsar rothschildi, and Black-winged Starling Sturnus melanopterus in increasing numbers.Several of this species are classed as threatened and continue to be taen from the wild (shepard 2006). Indeed supplies white-rumped shama increased as the expansion of illegal logging in the late 1990s opened new areas for trapping.at present the picture concerning aquistion of breeding stock is complex.most breeders prefer to exchange breeding stock within their networks but many will buy wild caught birds on occasions. some of these such as shamas may be recently taken from the wild whilst others notablly long-lived species such as straw-headed bulbul are purchased from bird-kepers and may have been caught from the wild up to 20 years previously.
Five general business models for breeding birds were identified during the survey: i) independent breeder; ii) breeder with out-sourcing; iii) breeder association; iv) village co-operative and v) commercial-scale bird farm.In addition, huge numbers of ‘amateur’ bird-keepers breed and sell the common domestic species: Canary, lovebirds and Budgerigar Melopsittacus undulatus.The first three types of enterprises are the locus [source?] of innovation on techniques to breed and rear songbirds. Central to each is a technically adept individual who has a passion for developing new breeding and husbandry techniques.New techniques are shared between breeders at workshops convened by Pelestari Burung Indonesia (PBI). These business modules are suited to rapid expansion and scaling up.
Important aspects of the bird-keeping hobby are governed by PBI. For instance, since the 1980s, PBI has trained and accredited songbird competition judges and most competitions seek PBI endorsement (use of their logo) as this brings status and an assurance of impartiality and integrity to their event.More recently, PBI has been actively expanding its breeder membership and organizing workshops and training events to promote knowledge-sharing and the creation of active breeder networks.
Developing a bird a certification system
The questionnaire survey revealed positive or ambivalent attitudes towards certification among bird keepers.The authors' research identified six communities of practice within and interacting with bird keeping, namely: i) organizers of songbird contests and prominent hobbyists; ii) breeders and breeder associations; iii) manufacturers of bird food; iv) journalists and editors in the bird-keeper media; v) the governing committee of PBI; and vi) conservationists within the international bird conservation community associated with Burung Indonesia (BirdLife Indonesia).
Representatives of each community came together in a series of three regional workshops held in Yogyakarta (Central Java), Surabaya (East Java) and Jakarta (West Java) during December 2007. The workshops were independently facilitated by the social enterprise, Aksenta, who specialize in strategy facilitation, certification and accreditation. The goal of the workshops was to prepare the public for the concept of certification, build trust and communication between different communities of practice and identify points in bird supply chains that could be certified.
Participants at these workshops were enthusiastic about the idea of certification and proposed that a working group be formed to work up the details. The working group met in February and March 2008. Their deliberations were informed by a review of international certification schemes, relevant Indonesian law and Aksenta experience of ISO9000 (a family of standards for quality management systems), forest and coffee certification. The Species Unit with the Department of Forest Protection and Nature Conservation (PHKA) were kept informed of progress but not directly involved in the process.
Elements of a proposed certification system
The certification systems will focus on songbirds with the following agreed objectives:1) to guarantee the captive-bred status of birds produced by certified breeding facilities; 2) to promote best practice in bird breeding both in terms of quality, welfare and quantity; 3) to accelerate the replacement process of wild-caught birds with captive-bred birds for pets or other purposes.There are three groups of songbirds with different certification requirements: i) native song birds; ii) non-native songbirds (canary and lovebird) which are bred locally; and iii) chicks of Orange-headed Thrush which are harvested from agroforests in Bali [Jepson 2008] .Developing standards and criteria for certifying the first two groups was the goal of the working groups. The object of the certification system will be the bird-breeding business unit (not the birds) and will cover all the bird breeding business models listed above. The system will focus on the production process (input–output); a measuring and monitoring system; and documentation that allows for a traceable system.
A stepwise approach to the development and introduction of certification is planned. This reflects current administrative and breeding capacity and the need to expand the number of breeders. It also aligns with the PBI policy that classes for wild-caught songbirds will be prohibited from PBI-accredited songbird contests after 2012.Initially, the songbird certification body will be hosted by PBI as a “Certification Committee”. This was approved at the PBI national meeting in March 2008 and will provide the new entity with credibility and administrative support. The Certification Committee will issue certificates to songbird breeders that have been independently audited against two basic criteria, each with indicators and standards. These are: suitability and competency of breeding facility; and assurance that birds produced are captive-bred at the facility. Auditors must complete training and pass a competency test, be registered, and agree to abide by a code of ethics.In addition,they should be knowledgeable about bird-breeding and the songbird hobby.
The intention is to fund a certification system through a combination of fees from bird breeders and sponsorship. Many breeders are small businesses so the system will be affordable but not free, pricing systems will reflects the number of breeding pairs and extent of production, and groups of breeders will be assessed during one audit. The certification committee hopes to secure additional funding from songbird contest organizers and the companies producing bird food and products.
Prognosis and next steps
The certification system outlined represents a starting point.It may change and evolve as it is introduced.The next step is to conduct pilot audits/certifications of bird breeders breeding different species in different regions of Java.There are a number of questions that still need to be thought through; for instance, if the ultimate goal is to provide consumers with a means to identify a bird of captive-bred origin (for example, with a ring) should certification extend to canary, lovebirds and budgerigars which are already bred in large numbers by bird keepers.The authors are of the opinion that this should not be the case, or should not happen because people already class these birds as ‘imports’ and semi domesticated species.They also believe it will be necessary and possible to extend certification to the harvesting of chicks as is occurring on Bali, but that different criteria and standards will be needed to control harvesting practice and stimulate breeding initiatives.
Gaining momentum for the establishment of a bird certification scheme will require the leadership and commitment of a number of people and groups within the world of bird keeping, breeding and conservation.Certification and moving to captive-bred birds supports the agendas of many interests and is not necessarily counter to others.In addition, the judges of songbird contests are already accredited by PBI so the general principle is not new within the hobby.There is a good chance that this work will translate from the conceptual stage into reality, especially if funds for some pilot certification can be secured.
References
BirdLife International (2001) Threatened Bird of Asia:the BirdLife International Red Data Book. BirdLife International, Cambridge, UK.
Jepson, P. (2008). Orange-headed thrush Zoothera citrina and the avian X-factor. Birding Asia 9:58-61.
Jepson, P., and Ladle, R. (in press). Developing New Policy Instruments to Regulate Consumption of Wild Birds: Socio-Demographic Characteristics of Bird-Keeping in Java and Bali. Oryx.
Jepson, P., and Ladle, R.J. (2006). Bird keeping in Indonesia: conservation impacts and the potential for substitution-based conservation responses. Oryx 39:442-4
Jepson, P. Ladle, RJ and Sujatnika (in prep) Re-framing bird-trade policy approaches: an economic profile of bird-keeping in Java and Bali, Indonesia
Shepherd, C.R. 2006 The bird trade in Medan, north Sumatra: an overview. Birding Asia 6: 16-24
Acknowledgements
The information summarized in this article is the result of collaborative action research involving the Oxford University Centre for the Environment, Nielsen-Indonesia, Burung Indonesia, Pelestarian Burung Indonesia and Aksenta. The research was funded by Defra’s Darwin Initiative - which draws on the wealth of biodiversity expertise within the UK to help protect and enhance biodiversity around the world. The authors thank Nielsen Indonesia for their invaluable assistance with the questionnaire surveys.The methodologies underpinning the figures in this article along with precise figures will be published in a series of forthcoming articles in the academic conservation literature.
Paul Jepson, OxfordUniversity Centre for the Environment, South Parks Road, Oxford, UK
Made Prana, Pelestari Burung Indonesia, co [c/o?] Taman Burung TMII, Jakarta13560, Indonesia
Sujatnika, Aksenta, Jl. Gandaria VIII/10 Kebayoran baru, Jakarta 12130
Fahrul Amama, Burung IndonesiaJl. Dadali 32, Bogor - Indonesia
JAMBI, RABU - Penangkaran species burung murai batu yang sempat dikembangkan Balai Konservasi Sumber Daya Alam (BKSDA) Provinsi Jambi beberapa tahun tahun lalu akhirnya gagal, karena kurang mendapat dukungan dana dari pemerintah pusat dan daerah.
"Semula penangkaran burung murai batu yang mulai langka di Jambi itu sempat berhasil, namun akhirnya gagal karena terbentur dana," kata Kepala BKSDA Provinsi Jambi, DR. Ir. Didy Wurjanto, M.Sc di Jambi, Rabu (24/12).
Species tersebut mulai langka atau terjadi penurunan populasi yang cukup tajam selain kerusakan hutan juga tingginya penangkapan dan minat masyarakat penggemar burung berkicau di Jambi untuk memeliharanya.
Populasi murai batu kini hanya ditemukan di kawasan pedalaman hutan konservasi seperti Taman Nasional Kerinci Seblat (TNKS), Taman Nasional Bukit Dua Belas (TNB) dan Taman Nasional Berbak (TNB). Itupun jumlahnya tidak seberapa.
BKSDA Jambi hingga kini belum memiliki data yang pasti jumlah populasi species murai batu, sehingga perlu dilakukan penelitian. Para penggemar burung berkicau di Jambi sampai kini juga belum ada yang berhasil menangkarkan murai batu berwarna kuning dan hitam, karena untuk memeliharanya saja juga amat susah atau perlu ketelatenan agar bisa bertahan hidup lama.
"Kami berharap ada masyarakat penggemar burung berkicau mengembangbiakan murai batu, seperti Jalak Bali kini telah berhasil dikembangbiakan masyarakat di Bali dan Jawa. BKSDA Jambi akan membantu dari segi teknis pengembangbiakannya," tambahnya.
Species burung murai batu itu memungkinkan bisa dikembangbiakkan masyarakat, terutama para penggemar burung berkicau, lain dengan satwa langka lain seperti harimau Sumatera (Phantera tigris sumaterae) diburu dengan membunuh karena beberapa bagian tubuh akan dijual dengan harga mahal ke luar negeri.
Harga burung murai batu yang diperjualbelikan di pasar lokal Jambi rata-rata Rp300.000-Rp500.000 per ekor. Jika kicauannya sudah jadi harganya bisa mencapai Rp1,5 juta hingga Rp2 juta per ekor. Udin, salah seorang penjual burung murai batu di Jambi mengatakan, untuk mendapatkan burung tersebut di hutan Jambi kini semakin sulit.
"Anak buah saya terkadang bisa seminggu sampai dua minggu berada di hutan mencari murai batu, itupun hasilnya tidak memuaskan terkadang sama sekali tidak dapat," katanya.
Peningkatan manfaat sosial dan ekonomi dari hobi pemiliharaan burung kicauan dan mengurangi dampak pemeliharaan burung kicauan terhadap populasi burung di alam
Fahrul P. Amama
Indonesia telah lama dikenal dengan kekayaan keanekaragaman hayatinya. Di antara kekayaan keragaman satwanya, burung merupakan salah satu kekayaan hayati yang paling menakjubkan. Indonesia memiliki sekitar 1593 jenis burung yang menempatkan Indonesia sebagai nomor empat terbanyak di dunia. Lebih menakjubkan lagi, 353 jenis di antaranya merupakan jenis unik dan endemik (hanya terdapat di Indonesia), yang membuat Indonesia melesat ke posisi nomor satu di dunia dalam hal keanekaragaman jenis burung endemik. Namun sayangnya, keanekaragaman jenis burung yang kita miliki semakin terancam keberadaannya. Saat ini terdapat 119 jenis burung yang terancam punah sehingga menempatkan Indonesia sebagai negara yang burungnya paling banyak terancam punah. Sementara sekitar 195 jenis burung lainnya tengah antre sebagai jenis burung yang mendekati terancam punah. Kondisi ini tidaklah makin membaik dari waktu ke waktu. Pada tahun 1994 di Sumatera tercatat sebanyak 26 jenis burung terancam punah. Jumlah ini meningkat pada tahun 2001 menjadi 195 jenis. Ada beberapa penyebab terancam punahnya berbagai jenis burung di Indonesia. Antara lain adalah hilangnya habitat, terutama habitat hutan, yang menjadi tempat hidup burung. Luas hutan yang hilang di Sumatera dalam kurun waktu 1985-1997 mencapai angka 67.000 km2, sementara Kalimantan lebih parah lagi karena telah kehilangan 90.000 km2 kawasan hutannya. Dari 16 juta hektar luas hutan yang dimiliki Sumatera pada tahun 1900, kini tinggal tersisa hanya sekitar 300.000 hektar. Ancaman lainnya adalah penangkapan, perdagangan serta penyelundupan burung-burung terutama jenis-jenis eksotis seperti paruh bengkok. Di kawasan timur Indonesia, ribuan ekor nuri dan kakatua ditangkap setiap tahunnya untuk diperdagangkan. Sebagian besar diselundupkan ke luar negeri, sebagian lainnya dipasok untuk memenuhi permintaan pasar domestik.
Dampak Hobi Memeliharaa Burung di Perkotaan Hobi memelihara burung yang berkembang di Indonesia juga memberi dampak yang cukup signifikan terhadap kelestarian jenis burung. Hasil survey yang telah dilakukan oleh Burung Indonesia bersama Universitas Oxford dan Darwin Initiative, bekerja sama dengan The Nielsen menunjukkan,1,486,000 burung tangkapan dari alam dipelihara di enam kota besar di Jawa dan Bali. Survey yang sama juga memperlihatkan bahwa dari total jumlah burung kicauan yang dipelihara, lebih dari setengah (58%) merupakan jenis hasil tangkapan dari alam. Sementara sepertiga diantaranya (32%) merupakan jenis domestik. Hanya sekitar 8% yang merupakan jenis yang sebagian telah ditangkarkan, dan cuma 2% yang merupakan jenis yang sekarang banyak ditangkarkan. Berdasarkan hasil analisis di empat kota besar di Jawa, ditemukan pula bahwa terjadi peningkatan jumlah burung kicauan lokal yang dipelihara dari hasil tangkapan di alam. Pada tahun 1999 jumlahnya mencapai 738.518 ekor sementara pada tahun di tahun 2006 jumlahnya meningkat menjadi 878.077 ekor. Untuk beberapa jenis burung, penangkapan di alam bisa menyebabkan jenis ini semakin sulit ditemui. Banyak jenis burung yang dahulunya sangat umum dijumpai menjadi semakin kecil populasinya di alam sehingga semakin langka karena banyak ditangkap dan diperdagangkan. Sebut saja sebagai contoh: cucak rawa, murai batu, jalak suren dan anis kembang. Lebih celaka lagi, jenis-jenis yang banyak diburu untuk dijadikan klanengan dan pelomba itu bukan termasuk jenis burung yang dilindungi. Kalaupun jenis tersebut kemudian dilindungi, upaya penegakkan hukum juga belum tentu efektif. Sementara populasi di alam tetap semakin rentan, sehingga diperlukan upaya pemulihan populasi tersebut.
Pendekatan Baru Untuk Pelestarian Burung Burung Indonesia sebagai lembaga konservasi memiliki misi utama menjaga keragaman burung Indonesia dan habitatnya, serta bekerjasama dengan masyarakat untuk mencapai pembangunan yang lestari. Disadari bahwa selama ini upaya-upaya yang dilakukan untuk menjaga kelestarian jenis-jenis burung di Indonesia masih belum efektif. Karena itu perlu dikembangkan pendekatan-pendekatan baru dalam upaya pelestarian jenis burung sehingga tujuan melestarian keragaman burung di Indonesia dapat dicapai melalui cara-cara yang efektif. Selama ini pendekatan yang lebih banyak digunakan untuk melestarikan keragaman jenis burung adalah pendekatan regulasi. Strategi utama pendekatan ini adalah menghentikan atau membatasi pasokan burung/satwa dari alam melalui peraturan eksternal dan penegakan hukum. Pendekatan ini seperti memutus rantai pasar dari produsen/pemasok kepada konsumen/pembeli. Pendekatan regulasi banyak digunakan untuk menghentikan perdagangan daging satwa liar dari alam, perdagangan harimau, maupun perburuan gading gajah untuk dijual. Komponen utama dari pendekatan ini tentunya penegakkan hukum yang efektif, tidak pandang bulu, serta memberikan efek jera bagi pelaku. Sayangnya penegakkan hukum untuk kejahatan hidupan liar (wildlife crime), seperti juga bagi kejahatan di bidang lainnya, hingga saat ini masih sangat lemah. Pertanyaan yang kemudian muncul adalah, apakah pendekatan regulasi ini cocok dan tepat untuk diterapkan begi semua jenis burung, terutama burung kicauan? Untuk menjawab pertanyaan ini, Burung Indonesia bekerjasama dengan the Nielsen, PBI dan Aksenta melakukan studi cukup mendalam mengenai aspek hobi memelihara burung kicauan yang berkembang di Indonesia. Studi ini mencakup survey kuesioner di enam kota besar di Jawa dan Bali, analisis rantai pasar dari perdagangan burung liar dari pasokan alam di Sumatera dan Kalimantan, serta studi mengenai penangkaran burung kicauan yang berkembang di beberapa kota di pulau Jawa.
Hasil Survey Kuesioner di Enam Kota Besar di Jawa dan Bali Burung Indonesia bersama Universitas Oxford, Darwin Initiative, dan Nielsen pada akhir tahun 2006 melakukan serangkaian penelitian mengenai hobi memelihara burung dalam sangkar (bird keeping) yang sangat jamak di negeri ini. Survei dilakukan di enam kota besar yang dinilai representatif yakni Jakarta, Bandung, Yogyakarta, Semarang, Surabaya, dan Denpasar. Hasilnya, burung adalah satwa yang paling banyak dipelihara keluarga Indonesia. Dari 1.781 rumah tangga di kota-kota besar itu, sebanyak 636 atau sekitar 36 persen rumah tangga memilih burung sebagai binatang peliharaan. Artinya, bisa diasumsikan kalau 1.486.611 rumah tangga di enam kota besar seantero Jawa-Bali yang memelihara burung. Ini adalah angka terbesar dibanding data hewan peliharaan lain. Ikan hanya dipelihara oleh 434 rumah tangga atau sekitar 24 persen, kucing hanya dipelihara 228 orang (13 persen), dan anjing dipelihara 179 rumah tangga atau sekitar 10 persen. Sisanya dengan persentase yang relatif kecil sekitar satu sampai lima persen adalah reptil, monyet, dan binatang-binatang yang dipandang langka dan unik lainnya. Fakta ini tidak lepas dari budaya memelihara burung yang telah mengakar kuat dalam sanubari masyarakat, terutama kalangan masyarakat Jawa. Budaya Jawa yang mendasarkan kekuatan jiwa pada lima hal – yang salah satunya adalah burung – itulah yang melatarbelakangi banyak orang Jawa memelihara burung. Dari survey juga terungkap, alasan utama banyak orang memelihara burung adalah burung mengingatkan pemeliharanya akan suasana asri di kampungnya. Burung juga menjadi sarana yang baik dalam memperluas dan mempererat pertemanan di kalangan masyarakat penghobi. Di samping itu, hobi memelihara burung juga meningkatkan minat serta pengetahuan mereka mengenai berbagai aspek pada burung kicauan. Kalangan penghobi burung juga merasakan berbagai manfaat dalam menekuni hobi mereka. Salah satunya adalah melepaskan stress dan membuat suasana lebih santai di rumah. Selain sebagai kegiatan pengisi waktu luang, burung juga merupakan bahan pembicaraan yang menyenangkan bagi kalangan penghobi dalam mempererat persahabatan dan kekeluargaan. Dari segi ekonomi, hobi memelihara burung juga memberikan dampak yang sangat signifikan bagi masyarakat. Rata-rata penghobi mengeluarkan uang sekitar 1,5 juta rupiah setiap tahunnya untuk burung kicauan. Hasil penelitian menunjukkan bahwa perputaran uang dalam hobi burung kicauan per tahunnya mencapai 800 Milyar rupiah. Tak hanya dari segi besaran rupiahnya, perputaran uang dalam hobi burung kicauan juga memberikan multipyer efek yang sangat signifikan bagi masyarakat luas. Perputaran uang dalam satu even lomba saja dapat mencapai 500 juta rupiah. Fakta di lapangan menunjukkan bahwa keberadaan lomba tersebut membuka peluang usaha bagi sektor informal seperti pedagang kaki lima, perajin sangkar, penjual pakan hidup dan usaha lainnya. Dalam sektor penangkaran burung sebagai salah satu pemasok burung kicauan, juga terlihat banyak peluang bagi masyarakat untuk meningkatkan pendapatannya sebagai penangkar, pengumpul pakan hidup, hingga perawat anakan yang bertugas melolohkan makanan. Sektor ini juga membuka peluang bagi masyarakat di desa untuk tetap memperoleh pendapatan yang signifikan pada usia yang dianggap sudah non produktif.
Pendekatan Pasar dan Sistem Sertifikasi Kesimpulan yang dapat diambil dari studi tersebut adalah hobi memelihara burung kicauan memberikan keuntungan sosial, budaya dan ekonomi yang signifikan. Namun di sisi lain, hobi memelihara burung juga memberikan dampak pada populasi burung liar jika pasokan burung hanya diambil dari alam. Untuk itu diperlukan pendekatan yang berbeda dalam upaya pelestarian burung, yakni pendekatan pasar. Pendekatan pasar bertujuan memodifikasi rantai pasokan dengan kontrol pasar (market ‘pulls’ & pushes). Pendekatan ini lebih menitikberatkan kepada kesadaran para pelaku pasar serta karisma. Dengan pendekatan ini, rantai pasar tidak diputus seperti yang dilakukan pada pendekatan regulasi. Modifikasi rantai pasokan dilakukan untuk menjamin keberlangsungan rantai pasar itu sendiri. Modifikasi ini dilakukan dengan merubah pasokan langsung dari alam dengan tiga komponen. Komponen pertama adalah bahan pengganti. Contoh nyata dari komponen ini adalah kayu hitam (ebony) dan gading gajah (ivory) yang menjadi bahan utama pembuatan piano. Dengan digantikannya bahan tersebut dengan plastik, otomatis mengurangi permintaan terhadap gading gajah dan kayu hitam dari alam. Komponen kedua adalah pemanfaatan berkelanjutan. Komponen ini tidak menghentikan pasokan dari alam, tetapi proses pemanenan dari alam dibatasi serta dikontrol sehingga tidak mengancam keberlanjutan jenis yang dipanen. Pembatasan dapat berupa masa pemanenan, jumlah kuota pemanenan serta spesifikasi jenis yang boleh dipanen (ukuran, usia dan lainnya). Komponen lainnya adalah pembiakan/penanaman, yang untuk dunia satwa dikenal dengan penangkaran. Komponen ini sangat penting untuk perlahan-lahan menggantikan ketergantungan terhadap pasokan langsung dari alam. Sehingga pengambilan langsung dari alam nantinya dapat sangat dibatasi, misalnya hanya untuk dijadikan indukan bagi penangkaran. Ketiga komponen tersebut juga dikontrol dalam rantai pasar dengan menggunakan sertifikasi. Dengan demikian dampak negatif terhadap populasi di alam dapat dikurangi tanpa memutus rantai pasar. Dalam pendekatan ini sertifikasi menjadi komponen penting dalam memodifikasi rantai pasar sehingga dapat menjamin keberlanjutan. Berbagai kalangan penghobi burung kicauan kini sedang mendiskusikan kemungkinan untuk mengganti penangkapan di alam dengan budidaya/penangkaran. Untuk itu perlu dilakukan penandaan sehingga dapat dibedakan burung hasil tangkaran dengan burung hasil tangkapan alam. Untuk menjamin keabsahan penandaan tersebut dibutuhkan sistem sertifikasi bagi burung hasil tangkaran. Salah satu kemungkinan adalah membentuk suatu sistem dimana anakan burung hasil budidaya akan ditandai dengan cincin khusus yang akan membuktikan bahwa burung tersebut adalah hasil dari penangkaran. Cincin khusus ini disebut cincin tertutup (close ring) yang sifatnya permanen. Ukuran cincin tersebut disesuaikan sedemikian rupa berdasarkan ukuran kaki jenis burung tertentu sehingga hanya dapat dipasang di kaki burung pada saat masih anakan. Tujuannya sertifikasi dan pencincinan ini adalah supaya orang dapat membedakan antara burung hasil penangkaran dengan hasil penangkapan di alam. Dengan demikian konsumen dapat memilih untuk membeli burung hasil tangkaran jika diinginkan. Diharapkan dengan adanya sertifikasi dan pencincinan ini para penghobi burung kicauan dapat mengambil bagian dalam upaya mengurangi pengaruh hobi memelihara burung terhadap populasi burung di alam.
Fahrul P. Amama bekerja di Knowledge Center Burung Indonesia sebagai Social Marketing and Campaign Officer.
Bird-keeping is an extremely popular pastime in Indonesia, where there is a thriving internal market in both wild-caught and captive-bred birds. However, little is known about whether the scale of bird-keeping represents a genuine conservation threat to native populations. Here we present the results of the largest ever survey of bird-keeping among households in Indonesia’s five major cities. Birds were found to be urban Indonesia’s most popular pet (kept by 21.8% of survey households) and we conservatively estimate that as many as 2.6 million birds are kept in the five cities sampled. Of bird-keeping households, 78.5% kept domestic species and/or commercially bred species and 60.2% kept wild-caught birds that we classified into three conservation categories: native songbirds, native parrots and imported songbirds. Compared to non-bird owners, households keeping wild-caught birds in all three conservation categories were richer and better educated, whereas households owning commercially-bred species were richer but not better educated and households keeping domestic species did not differ in educational or socio-economic status. We conclude that bird-keeping in Indonesia is at a scale that warrants a conservation intervention and that promoting commercially-bred alternatives may be an effective and popular solution.
Keywords Birds, bird trade, CITES, culture, Indonesia, market-led conservation.
Introduction
The international conservation movement is unified in the belief that human use and trade of wildlife should not endanger wild populations. This principle found widespread support among governments of the community of nations and is the basis of the 1973 Convention on Trade in Endangered Species (CITES Secretariat, 2000). This convention promotes legal and regulatory mechanisms as the means to put this principle into practice. A central feature of the treaty is three lists of species at risk from trade (Appendices I–III), which establish increasingly stringent international trade restrictions on the species concerned. In many less-developed countries assuring CITES compliance is the primary driver of national level policy meetings on wildlife trade. Consequently CITES regulatory discourse tends to dominate the thinking of local policy makers and frame how they conceptualize responses to both international and domestic wildlife trade (Reeve, 2002). To avoid perpetuating the misconception that trade (regulatory) measures alone constitute an effective policy response when a species is threatened by trade (Dickson, 2003), we suggest that more debate is needed on the efficacy of market-led approaches in less-developed countries.
Two such market-led approaches gaining widespread acceptance are sustainable offtake and substitution, either with cultivated or farmed wild species or alternative products. These measures have been applied to major extraction industries such as forestry (timber, non-timber forest products; Shanley et al., 2002), fisheries (MSC, 2002), ‘collectables’, notably orchids (Orlean, 2000), medicinal plants (Schippman et al., 2002) and the aquarium-fish sector (Wabnitz et al., 2003). They incorporate the recognition that for some commodity chains it is impractical and/or undesirable on social, cultural and economic grounds to ban trade and consumption of natural products. In addition they reflect the rise of ‘sustainability’ in international policy discourse (Princen & Finger, 1994) and the idea of ethical or ‘green’ consumerism that posits that supply chains can be changed by empowering consumers to make informed and ethical decisions over which products or brands they purchase.
Capture for the pet trade is the primary threat category for 34 bird species in Asia and is a major problem for several threatened birds in Indonesia (BirdLife International, 2003). Bird-keeping is a popular pastime in Indonesia, with deep cultural roots. It is widely assumed that the hobby negatively affects wild populations of common as well as threatened birds (Nash, 1994) and that government capacity and will to implement wildlife regulations in Indonesia is limited (Reeve, 2002).
Fig. 1 Map of West Indonesia with locations of the five cities surveyed.
Here we consider three questions. Firstly, is birdkeeping in Indonesia at a scale where it constitutes aconservation issue? Secondly, is substitution already occurring and at what level? Thirdly, is the profile of Indonesian bird-keepers compatible with a successful substitution mechanism (i.e. promoting commerciallybred alternatives)? We argue that complementary approaches to regulation are needed where bird-keeping has deep cultural roots, and that substitution is more likely to succeed in situations where a degree of commercial breeding already exists, where commercial breeding produces birds cheaper or of better quality compared to catching from the wild, and where the hobbyists are from social strata that can be targeted by ethical consumerist propaganda. To investigate these questions and propositions we conducted an exploratory survey of bird-keeping in Indonesia’s five major cities.
Methods
The present survey was piggy-backed on the March 1999 biannual OmnibusTM household survey conducted by the consumer survey company A.C. Nielsen. This survey samples a population of 1,740 randomly selected households in Jakarta, Surabaya, Medan, Bandung and Semarang (Fig. 1). These are Indonesia’s five most populous cities and together support a population of c. 20 million people (one third of the urban population of west Indonesia) residing in an estimated 4,342,000 househoulds (A.C. Nielsen, own data). The survey protocol involves a face-to-face questionnaire interview with the person responsible for choosing the household’s needs, and covers a variety of topics of interest to retail companies. Socio-economic attributes are collected on each respondent such as, age, education and monthly household income (grouped in five bands). Within this regular survey we inserted a set of questions relating to bird-keeping. Respondents were first asked whether or not they kept a pet. Those who responded that they kept a bird were asked four supplementary questions: (1) What birds do you keep? (2) How many birds do you keep? (3) How long do the birds live? (4) Where do you obtain your birds? Because of the short time available for this topic within the overall interview, respondents were given pre-defined response categories for questions 1 and 4 with the opportunity to define ‘others’. The predefined response categories related to five bird groups and species of particular interest for conservation planning at the time, namely: (1) spotted dove Streptopelia chinensis and zebra dove Geopelia striata, which are popular pets and are commercially bred; (2) laughing-thrushes Garrulax spp., of which several species are imported from China, Indochina and South-east Asia; (3) parrots, which mostly originate in eastern Indonesia and of which several species are kept; (4) hill myna Gracula religiosa, which was proposed for inclusion on CITES appendix II at the time of this survey (1998); and (5) straw-headed bulbul Pycnonotus eylanicus, which is close to extinction in the wild (BirdLife International, 2001). Respondents were asked for the names of any birds kept that they considered did not fit into one of these groups.
For the purpose of analysis, data was consolidated into five conservation impact categories: (1) domestic species, (2) commercially-bred native species, (3) wildcaught native songbirds, (4) wild-caught native parrots, (5) wild-caught imported songbirds (Appendix 1). Birds kept in categories 1 and 2 are of limited conservation concern, whereas keeping birds in categories 3–5 may result in negative conservation impacts. Allocation of respondent answers to each of these categories was reviewed by an independent expert on Indonesian birdkeeping and bird names (S. van Balen). In this survey chicken was treated as a category of pet different to a bird, in accordance with the folk taxonomy followed by many Indonesians who lack a biological training.
We generated an estimate of the total number of birds kept in each category by multiplying the number of households keeping a bird by the average number of birds kept. To generate an estimate of the number of birds acquired per year we first converted the response categories on length of time a bird was kept to an acquisition rate (i.e. a check in the 1–3 month category equates to 1 bird acquired per 3-month period, a check in the 3–6 month category equates to 0.5 birds acquired in a 3-month period, and so on), and then multiplied the mean acquisition rate for a category by the estimated number of birds kept.
Results
This survey found that birds are the most popular household pet in the sample population. In the five major cities, 21.8% (380/1,740) of households surveyed kept a bird, compared with 16.6% (289/1,740) keeping a chicken, 9.5% (165/1,740) a fish, 3.4% (9/1,740) a cat, and 2.7% (47/1,740) a dog. The frequency of bird ownership extrapolates to an indicative total of 1,261,600 households keeping a bird. The indicative number of birds kept in five conservation categories is 2,823,740 and the estimated number of birds acquired per year is 2,457,760.
The incidence of keeping of hill myna and straw-headed bulbul, which were species of particular conservation interest at the time of the survey, was low (n=8 and 15, respectively). Domestic and commercially-bred species account for 65.8% of the total (Table 1).
There were significant differences in the proportion of the sample population keeping birds in different cities (x2=69.358, n=1,360, df=4, P<0.001). In Jakarta (16.7%) and Medan (10.5%) the proportion of households is lower than predicted, whereas in Semarang (34.4%) and Surabaya (29.5%) it is higher than expected. The average number of birds owned also differed significantly between cities (F4,1735=18.459, P<0.001; Fig. 2) with Semarang (0.472 birds per person) the highest and Medan (0.1334) the lowest. Tukey-Kramer post-hoc tests revealed that Semarang and Surabaya have significantly more birds per household than Medan, Bandung and Jakarta (Fig. 2).
Respondents named 38 species or species groups as being kept in addition to the five predefined response categories (Appendix 1). Species in the two categories of least conservation concern were owned by 78.4% (298/380) of households keeping birds, whereas 60.2% (229/380) kept a species in the three categories of conservation concern (i.e. wild-caught). Native song-birds were by far the most popular category kept (86.8%, 330/380 of households keeping a bird) and the proportion classed as commercially-bred slightly exceeds that classed as wild-caught (44.5% vs 42.3%) (Table 1).
Table 1 Indicative number of birds kept and acquired in Indonesia’s five major cities according to five groupings of conservation concern.
Fig. 2 Mean numbers (PSE) of birds kept by households in Indonesia’s five largest cities.
Non-parametric bivariate analysis revealed consistent patterns in respondents’ socio-economic status, education, age group and bird ownership. Overall, households keeping birds had a higher household income and educational attainment but age group was not significantly different. Specifically, households owning a bird in the three conservation concern categories were richer and better educated, whereas households owning commercial-bred species were richer but not better educated, and households keeping domestic species did not differ from households not keeping birds (Table 2).
In the sample surveyed 56.1% (193/380) of respondents said they obtained their birds from a bird market or door-to-door seller (who work on behalf of market traders), 46.8% (178/380) from a friend or relative and 10% (38/380) said they caught their birds. We found no significant difference in the relative proportions of respondents obtaining their birds in these ways between the cities. However, analysis of the socio-economic attributes revealed that richer and more educated households buy from markets or door-to-door sellers, whereas poorer, less-well educated households are more likely to catch their birds. There were no significant differences between socio-economic attributes of households that did or did not obtain their bird as a gift or from a friend (Table 2).
Table 2 Results of bivariate analysis (Mann Whitney U tests) of socio-economic status (SES), educational background category and age group for the five conservation impact categories (see text for details).
Discussion
This survey constitutes the first empirical profile of the bird-keeping hobby in Indonesia. Considering that the five cities sampled in this survey account for just a quarter of Indonesia’s 80 million urban population, four important general conclusions can be drawn: (1) birdkeeping is a very popular hobby and retains a central place in the urban culture of modern Indonesia; (2) large numbers of birds are kept and acquired each year; (3) wild-caught birds account for about one third of birds kept and acquired; (4) bird ownership is generally associated with richer and better educated households.
The survey findings confirm the cultural significance of bird-keeping in Indonesia. In traditional Javanese culture a bird in a cage symbolizes the importance of a hobby in a balanced life and the symbolic species is generally considered a dove, either the zebra dove or the spotted dove (H.M. Kamil Osemann, pers. comm.). We found that these two species, which constitute our commercially-bred native species category, are kept by 56%of households keeping a bird.
Our finding that bird-keeping is most popular in Semarang is consistent with the thesis that bird-keeping is part of the Javan cultural identity. Semarang is located in central Java, considered to be the cultural heartland of the Javanese as it is the site of the ancient Majaphit kingdom and the cultural cities of Solo and Yogyakarta.
However, it is also important to note that Semarang has the highest proportion of ethnic Chinese of any city in Indonesia, and Surabaya (the second ranking city for popularity of bird-keeping) also has a large ethnic Chinese population (Oey, 1997). Bird-keeping is a traditional pastime in China and the combination of proximity to central Java and large populations of ethnic Chinese probably explains the higher than expected incidence of bird-keeping in these two cities. Conservation approaches that maintain and strengthen cultural practices are more likely to succeed. The Javanese and Chinese ethnicities are economically and politically the two most powerful groups in Indonesia and, in our view, they are more likely to support a market-led, as opposed to a regulatory-approach to reforming bird-keeping
because the latter could be perceived as an attack on or interference with their cultural identities.
Our findings suggest that c. 2.5 million birds are acquired by households each year, of which 758,250 are wild-caught native songbirds, 60,230 are wild-caught native parrots, and 146,210 are wild-caught imported songbirds. Considering that the five cities sampled represent only a quarter of Indonesia’s 80 million urban population and bird-keeping is also popular in rural areas, our figures suggest that Nash’s (1994) estimate of 1.3 million wild-caught birds per year may be conservative. However, we stress that our figures relate to birds acquired by a household and not from the wild. Long-lived species such as parrots may change hands several times before they die and in this category the number of birds taken from the wild may be substantially less than our indicative figure of 50,590 acquired per year. Conversely, mortality of wild-caught songbirds in the supply chain between the point of capture and purchase by a bird hobbyist is believed to be high and the indicative figure of c. 614,000 may be an underestimate of the birds taken from the wild.
Our survey lacks the precision to estimate the numbers of threatened or CITES-listed species involved. The list of species named by respondents suggests that bulbuls Pyconotus spp., starlings Sturnus spp. and whiterumped shama Copsychus malabaricus were among the more popular wild-caught native species kept. In the absence of data on populations of commoner species in Indonesia it is difficult to gauge the impact of birdkeeping on wild populations. However, common bird populations on Java have declined markedly in the last 50 years (Holmes, 1995) and a hobby on this scale must add a significant additional stress to these populations.
The large number of domestic and commercially-bred species kept show that substitution is already happening on a large scale. This is borne out by the fact that bird-farms (mostly located in East Java) were the fifth ranking buyer of magazine advertising space in 1999 (A.C. Nielsen, own data). Moreover, the large proportion of birds acquired as a gift or from a friend or relative suggests that small-scale breeding and exchanging of birds among hobbyists is widespread.
A key finding of this survey is that bird-keeping is commoner among richer households and that wildcaught species are kept more frequently in richer and better educated households. These households are easiest to reach and more likely to be swayed by social marketing techniques promoting commercially-bred alternatives. This is because hobbyists in these households are likely to buy specialist magazines, be members of clubs and societies, and more able and willing to make an ethical choice.
In summary, this study finds that bird-keeping among urban Indonesians is of a scale that warrants a conservation intervention and exhibits a profile that suggests substitution with commercially-bred alternatives would be an effective response. Two additional points merit note.
Firstly, whilst the cost of some wild-caught species is low that of several species of conservation concern is high. For example, at the time of this study straw-headed bulbuls were selling for USD 120, hill mynas for USD 85–250 depending on their vocal repertoire, and Zoothera thrushes for >USD 200 (Jepson et al., 1998; P. Jepson, unpubl. data; C. Trainor & I. Setiwan, pers. comm.). Whilst the breeding of many ‘soft-bill’ species is difficult, the value of some species and the size of the market may be sufficient to interest investors willing to overcome the technical challenges that commercial breeding of these species may pose.
Secondly, the bird-keeping hobby revolves around a sophisticated appreciation of bird song, form and coloration. Birds with a pedigree of winning song contests or with a novel vocal or physical characteristic are particularly sought after. For example, in 1998 hill mynas able to sing Ricky Martin’s World Cup theme song appeared on the market and fetched three or four times the normal price. Commercial breeding can produce birds with pedigree or vocabularies and endearing behaviours. Marketing such birds as a superior ‘product’ to a wild-caught bird would generate business as well as conservation benefits.
This survey did not provide sufficient data to design and develop a market-led response to mitigate impacts of the bird-keeping hobby on wild bird populations. Although our survey technique enabled a large population to be surveyed at low cost it lacked precision and deep insight. A dedicated survey adopting social marketing principles would be needed to design a campaign aimed at changing the culture of bird-keeping in Java. We suggest that this should include an attitude survey of hobbyists to ascertain their motivations and preferences, and to generate the knowledge base for a targeted social marketing campaign. This should be coupled with exploratory meetings with bird farms to ascertain the
feasibility of breeding species of conservation concern, their interest in doing so, and their readiness to engage with some sort of accreditation and labelling scheme that would provide assurance that wild-caught birds cannot enter the supply chain.
References
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Acknowledgements
We are indebted to Farquhar Stirling, Head of A.C. Nielsen Indonesia for making this survey possible and to Dindin Kusdinar also of A.C. Nielsen for a preliminary analysis of the data. Scott Guggenheim convinced PJ to seriously consider market-driven approaches during his time as coordinator of the BirdLife International – Indonesia Programmes (1991–1997). We thank Richard Noske, Susanne Schmitt, Iwan Setiwan, Ria Suryanthi, Darmawan and Robert Whittaker for comments on drafts of this manuscript.
Biographical sketches
Paul Jepson was formerly head of the BirdLife International-Indonesia Programme (1991–1997), which included a significant field and policy component on bird trade. His research interests include conservation governance, protected area policy and wildlife trade. He is leading a new project to assess the efficacy of market-led mechanisms to mitigate the conservation impacts of bird-keeping in Java, funded by the Darwin Initiative.
Richard Ladle is the Director of Oxford University’s MSc in Biodiversity, Conservation and Management. His research interests include the representation of conservation in the media, assessment of public attitudes to conservation and the environment, conservation biogeography, and the application of market-led solutions to environmental and conservation problems.
Paul Jepson (Corresponding author) and Richard J. Ladle Biodiversity Research Group & Environmental Change Institute, Oxford University Centre for the Environment, Dyson Perrins Building, Oxford, OX1 3QY, UK. E-mail paul.jepson@ouce.ox.ac.uk
Received 2 August 2004. Revision requested 10 November 2004. Accepted 7 February 2005.
