Bird Crime

Many raptor species are frequent victims of illegal human activity. Use of poison-baits in the countryside is one of the most widely used predator eradication methods worldwide (Márquez et al. 2012) and is a significant threat to biodiversity in the European Union. Poison is used to kill wildlife considered to be harmful to certain activities, in particular game management for hunting, livestock farming and other agricultural practices (Graham et al. 2005; Sotherton et al. 2009). Illegal use of poison is considered one of the most important issues regarding illegal killing of birds due to the serious conservation impacts (Margalida et al. 2008; BirdLife 2011) and is confirmed to be among the most important direct threats in Europe to the Spanish Imperial Eagle (Aquila adalberti), Eastern imperial eagle (Aquila heliaca), Red kite (Milvus milvus), and Egyptian vulture (Neophron percnopterus). Poison-baits have been identified, for example, as the primary limiting factor in the expansion of the reintroduced population of Red kites in northern Scotland (Smart et al. 2010) and of the UK Golden eagle (Aquila chrysaetos) population (Whitfield et al. 2008). In addition, poison- baits suppose a serious impacts on carnivore mammals (Virgós & Travaini 2005), by causing population decline and/or regional/national extinction of some species of bears, lynxes, wolves, mustelids or wild cats (Council of Europe 1993; Breitenmosser 1998; Lozano & Malo 2012; Ripple et al. 2014). Indiscriminate use of poison-baits also presents a risk to other wildlife, working animals (shepherd and hunting dogs), pets and human health, with potentially lethal consequences.

Very large numbers of birds are killed annually as a result of deliberate misuse or otherwise illegal use of poisons (Brochet et al. 2015; Bodega Zugasti 2014). This unnecessary mortality can severely affect the conservation status of vulnerable species, including species protected under national, EU and wider international law. A transboundary approach at EU level is needed to address this problem in the case of migratory species.

Use of poison-baits commonly involves lacing a food item in a toxic substance, normally phytosanitary products like insecticides, rodenticides, fungicides, herbicides or molluscicides (snail and slug pellets). The prepared bait is left in a spot accessible to the target animals and often to other non-target species, which may also be affected. Deliberate poisoning is therefore a large-scale, non-selective and destructive method of control that has a huge knock- on effect on non-target species; it may even pose risks to human health.

Illegal poisoning can involve legal everyday compounds which are used in an illegal manner, as well as substances which are illegal (e.g. Carbofuran or Aldicarb). The most common substances used in poison-baits are insecticides and, to a lesser extent, rodenticides, usually those that are known as highly toxic by users. Carbamate insecticides, such as carbofuran and aldicarb, are often used in poison-baits for predator control in numerous areas around the world. For example, in Spain, between 2005 and 2010, 50 % of cases of poisoning were caused by aldicarb and 22% of them by carbofuran (Bodega Zugasti 2012). In Hungary carbofuran was detected in 85% of the 476 birds found poisoned by baits to illegally control predators between 2000 and 2015. The other commonly detected chemicals in this country were terbufos (9%) and phorate (7%) (BirdCrime database of MME BirdLife Hungary).

Many of the Species Action Plans (around 50 bird species) developed by BirdLife International and funded by the EU, recognise poisoning as a threat and recommended anti- poisoning actions in most of the plans for raptors (e.g. both imperial eagles, all vultures or red kites).

Some raptors also fall victim to deliberate shooting, as they present a competition to hunters for small game species (Villafuerte et al. 1998). Sadly, many raptors are also just shot for sport and throphies.

In the year 2020, it is unacceptable that so many protected and endangered species are still being persecuted by humans. It is time to aggressively combat these illegal activities.



BirdLife. 2011. Review of the illegal killing and trapping of birds in Europe. European Conference on illegal killing of birds. Larnaca, Cyprus.

Bodega  Zugasti,  David  de  la.  2012.  Estudio  sobre  las  sustancias  que  provocan  el envenenamiento de fauna silvestre. Madrid: SEO/BirdLife,.

Bodega Zugasti, David de la (ED.).2014, Uso ilegal de cebos envenenados. Investigación y análisis jurídico. SEO/BirdLife-Proyecto Life+VENENO. Madrid.

Breitenmoser,  U.  1998.  Large  predators  in  the  Alps:  The  fall  and  rise  of  man's competitors. Biol. Conserv., 83, 279-289

Brochet et al. 2015. Preliminary assessment of the scope and scale of illegal killing and taking of birds in the Mediterranean. Bird Conservation Internacional (in press)

Council of Europe. 1993. Seminar on the biology and conservation of the wildcat (Felis silvestris). Council of Europe, Strasbourg.

Graham, Kate, Andrew P. Beckerman, and Simon Thirgood. 2005. Human–predator–prey  conflicts:  ecological  correlates,  prey  losses and  patterns  of  management. Biological Conservation 122, no. 2: 159-171

Lozano,  J.  &  Malo,  A.F.  2012.  Conservation  of  European  wildcat  (Felis  silvestris)  in Mediterranean  environments:  a  reassessment  of  current  threats. Mediterranean Ecosystems:  Dynamics,  Management  and  Conservation  (ed.  Williams,  G.S.).  Nova Science Publishers Inc., Hauppauge, pp. 1-31.

Margalida,  A,  R  Heredia,  M  Razin,  and  M  Hernández. 2008.  Sources  of  variation  in mortality  of  the  Bearded  vulture  Gypaetus  barbatus in  Europe. Bird  Conservation International 18, no. 1: 1

Márquez,  C.  J.  M.,  R.  Villafuerte  Vargas,  and  J.  E.  Fa.  2012.  Understanding  the propensity of wild predators to illegal poison baiting. Animal Conservation: 118-129

Ripple  W.J.,  Estes,  J.A.,  Beschta,  R.L.,  Wilmers,  C.C.,  Richie,  E.G.,  Hebblewhite,  M., Berger, J., Elmhagen, B., Letnic, M., Nelson, M.P., Schmitz, O.J., Smith, D.W., Wallach, A.D.  &  Wirsing,  A.J.  2014.  Status  and  ecological  effects  of  the  world’s  largest carnivores. Science, 343, 1241484.

Smart, Jennifer, et al. 2010. Illegal killing slows population recovery of a re-introduced raptor  of  high  conservation  concern–the  red  kite  Milvus  milvus. Biological Conservation 143.5: 1278-1286.

Sotherton, N, S Tapper, and A and Smith. 2009. Hen harriers and red grouse: economic aspects of red grouse shooting and the implications for moorland management. Journal of Applied Ecology 46, no. 5: 955-960

Villafuerte, R., J. Viñuela, and J. C. Blanco. 1998. Extensive predator persecution cased by population crash in a game species: the case of red kites and rabbit in Spain. Biological Conservation 84:181–188

Virgós, E. & Travaini, A. 2005. Relationship between Small-game Hunting and Carnivore Diversity in Central Spain. Biodivers. Conserv., 14, 3475-3486.

Whitfield, D P, Fielding, A H, McLeod, D R A and Haworth, P F. 2008. A conservation framework for golden eagles: implications for their conservation and management in Scotland.  Scottish  Natural  Heritage  Commissioned  Report  No.193  (ROAME  No. F05AC306).