Abstract
The chemical composition of non-lead, non-toxic, gunshot used for hunting waterfowl is regulated only in Canada and the USA. No nation regulates the composition of non-lead fishing weights, rifle bullets, and gunshot used for upland game hunting. Compositional criteria for these non-lead products are proposed here, based on established experimental toxicity protocols. Because of the demonstrated acute toxicity of ingested zinc shot to birds, fishing weights and gunshot should never be made of this pure metal. Nickel should be avoided as an incidental component of gunshot because of potential carcinogenicity concerns about such embedded shot in birds and other animals. These compositional criteria could be adopted by all nations undertaking the transition to non-lead fishing weights and hunting ammunition. The listed criteria would facilitate production and international trade in non-lead products, and promote easier enforcement and user compliance with non-lead standards.
Keywords: Bullets, Fishing gear, Regulations, Shot, Sinkers
Introduction
For centuries, metallic lead has been used in ammunition and fishing weights1 because of its availability and physical properties. The over two centuries of game shooting, especially with shotguns, has resulted in an enormous global accumulation of spent gunshot, estimated to be around 40,000 tonnes annually (Hansen et al. 2004). Spent lead gunshot and lost lead fishing weights remain in the environment, and resist corrosion for many years. A large body of scientific evidence shows that, globally, ingestion of spent leaded gunshot, bullet fragments, and fishing weights causes chronic and acute lead poisoning of both wildlife and humans (Franson et al. 2003; Watson et al. 2009; Delahay and Spray 2015; Arnemo et al. 2016; Grade et al. 2018). The toxicological impacts upon wild birds and the health impacts on humans who consume hunted game have caused hunting and fishing with lead products to be viewed as unsustainable (Kanstrup et al. 2018), and has led to the development of substitutes for both hunting ammunition and fishing weights. A transition to the use of non-lead2 products in wetlands is underway in 33 countries (23 total, and 10 partial bans) (Stroud 2015). This number may increase if the recommendation of the European Chemicals Agency of the European Commission (ECHA) that a transition to the use of non-lead ammunition for hunting in European wetlands becomes law. The Committee for Socio-Economic Analysis of the ECHA adopted, in June 2018, its final opinion to restrict use of lead-based gunshot in wetlands and wetland shot fall-out zones (SEAC 2018).
Many companies are involved with the manufacture and trade in shotgun and rifle ammunition and fishing weights, especially in Europe and the USA, and a growing number are involved with producing non-lead products. However, there is no international agreement on the chemical composition of non-lead products to ensure that they are non-toxic to animals that ingest them, and to the general environment into which they ultimately fall and remain. Only the USA and Canada have national legislation whose regulations require that candidate non-lead shot designed for waterfowl and coot hunting be tested scientifically to assess its toxicity to wildlife and other ecosystem components (USFWS 1997, 2013). There is no requirement for fishing weights, rifle bullets, and shotgun shot used for hunting non-wetland/non-waterfowl species to conform with that same toxicity testing in any nation, including the USA and Canada. By default, the only compositional criterion is that non-lead ammunition must contain less than 1% lead by mass, a condition of the US federal regulations (USFWS 1997).
There is no biochemical difference in the nature of lead toxicity in animals, whether the source of lead is gunshot, bullets, or fishing weights. However, a product that is “lead-free” may not be non-toxic when ingested. Thus, a common set of standards, applicable to ammunition and fishing weights, and internationally acceptable, would facilitate a transition to non-lead products at the manufacturing and enforcement levels. Much testing of the toxicity of the principal substitutes for lead gunshot has already occurred in the USA under federal regulation. This paper proposes using those and other published toxicity studies for the creation of compositional standards that can be applied readily to shot, bullets, and fishing weights, and be reflected in new regulation.
Prevailing metals and materials used in lead substitutes
The metals used in place of lead are selected according to their availability, density and other physical properties, ballistic suitability, ease of manufacture, and costs, and demonstrated non-toxicity to animals under specified conditions. These comprise iron (Fe), tungsten (W), bismuth (Bi), tin (Sn), and copper (Cu). Steel shot is widely used as a substitute for lead gunshot and is annealed soft iron that may contain approximately 1% or less carbon. Tungsten can be made into shot either as a mixture of powdered metal mixed with a high-density plastic polymer (95%W + 5% polymer), or as a composite mixed (sintered or alloyed) with other metals. Powdered tungsten can be mixed with a soft polymer putty that can be squeezed around fishing lines, and then be removed and re-used later. Tungsten powder can also be mixed with hard plastic polymers and shaped into many forms designed for use as fishing weights. Bismuth is alloyed with 3–6% tin to reduce the frangibility of the bismuth, whether used as shot or fishing weights. Pure tin has been used for small fishing weights, its malleability enabling it to be clamped repeatedly on and off fishing lines. Its low density (7.31 g/cm3 vs. 11.3 g/cm3 for lead) does not predispose it to use as gunshot or bullets. Pure copper (density 8.96 g/cm3) is used in hunting bullets and slugs fired from shotguns. Copper can be alloyed with approximately 5% zinc to make similar non-lead bullets. Bronze is an alloy of approximately 90% copper and 10% tin. Powdered bronze can be sintered with tungsten powder to make a hard, high-density tungsten-bronze gunshot.
The list of lead substitutes for gunshot has not changed in the past decade. This is because the most likely substitute materials and their suitability for gunshot have already been proposed and evaluated in North America. The same materials can be used for fishing weights, as can other materials which have not undergone any evaluation. Rifle bullet composition has not been subject to any regulation, other than the US default position that it contains less than 1% lead.
Listing of approved non-lead, non-toxic, shot formulae
Eleven distinct shot types have been given unconditional approval in the USA for hunting waterfowl (USFWS 2006) (Table 1). Presently, not all of these shot types are in commercial production. The North American and European markets are dominated by steel shot use because of price and availability. Other less-common types of non-lead shot include bismuth-tin shot, Tungsten-Matrix® shot, and Hevi® shot made from tungsten and other metals. High world market prices for tungsten are reflected in the highest prices of loaded cartridges. Bismuth and tin also cost more than iron, this also being reflected in higher prices than for steel shot cartridges (Thomas 2015a). However, mechanisms other than the cost of single cartridge components, including production volume and demand, influence the price of the final product.
Table 1.
Approved shot types | Composition by weight |
---|---|
Bismuth-tin | 97% bismuth and 3% tin |
Iron (steel) | Iron and carbon |
Iron-tungsten | Any proportion of tungsten and ≥ 1% iron |
Iron-tungsten-nickel | ≥ 1% iron, any proportion of tungsten, up to 40% nickel |
Tungsten-bronze |
51.1% tungsten, 44.4% copper, 3.9% tin, and 0.6% iron and 60% tungsten, 35.1% copper, 3.9% tin, and 1% iron |
Tungsten-iron-copper-nickel | 40–76% tungsten, 10–37% iron, 9–16% copper, and 5–7% nickel |
Tungsten-matrix | 95.9% tungsten and 4.1% polymer |
Tungsten-polymer | 95.5% tungsten and 4.5% Nylon 6 or 11 |
Tungsten-tin-iron | Any proportions of tungsten and tin and ≥ 1% iron |
Tungsten-tin-bismuth | Any proportions of tungsten, tin, and bismuth |
Tungsten-tin-iron-nickel | 65% tungsten, 21.8% tin, 10.4% iron, and 2.8% nickel |
This includes steel shot coated with a thin layer of copper or zinc
The presence of iron in the composition of six of the 11 formulae is intentional. It is to make the shot slightly magnetic so it can be distinguished from lead shot in the field by conservation officers enforcing non-toxic shot regulations. U.S. regulations require that approved shot types be distinguishable from lead shot, either by a portable electronic device, or by a demonstration of positive magnetism. Tungsten-polymer shot cartridges and bismuth-tin shot cartridges are distinguishable from lead shot cartridges in an electronic meter. Several of the approved shot types in Table 1 contain nickel. This metal has not been added for ballistic reasons. Tungsten-nickel alloys are used in making military penetrators, and the metal residues from machining the penetrators are, secondarily, converted into gunshot.
Steel shot may be coated with a thin layer of copper or zinc to inhibit rusting and is permitted under US regulations (USFWS 1997). The level of uptake of copper and zinc from the dissolution of these metals in the gut of birds from such a thin layer would be defined as non-toxic under the USFWS (1997) regulations.
Evaluation of the U.S. fish and wildlife service protocol and other non-lead products
Both the U.S and Canadian regulations for assessing the toxicity of candidate shot are based largely on results derived from experimentally ingested shot in game-farm ducks. The rigorous scientific testing of candidate shot under the Tier1, Tier 2, and Tier 3 components of the USFWS (1997, 2006) protocol means that the demonstrated non-toxicity of approved ingested shot can be largely accepted. The results of such toxicity testing have also been presented in the primary scientific literature for tungsten-based shot (Mitchell et al. 2001a, b, c) and further evaluated in Thomas et al. (2009) and Thomas (2015b). Shot made from bismuth-tin alloy is also fully approved as non-toxic (Table 1). Sanderson et al. (1997) demonstrated that ingested bismuth-tin shot did not have any toxic impact on the birds, and did not affect their reproduction.
Shotgun hunting causes many game birds and animals to be hit, but not killed (Norton and Thomas 1994; Hicklin and Barrow 2004; Falk et al. 2006), and then living with embedded shot. The issue of hunted species of animals containing embedded shot is important, because these animals, having recovered from their wounds, may live for many years with the shot material becoming solubilized and exerting potentially toxic effects. Assessing experimentally the toxicity for the target animal of such embedded shot is not part of the US and Canadian regulatory approval process. Sanderson et al. (1998) reported that shot made of bismuth-tin alloy implanted into the breast muscle of ducks did not induce toxic effects. A similar finding was reported by Kraabel et al. (1996) when shot made from tungsten-bismuth-tin was implanted into ducks. Shot made of bismuth-tin alloy was implanted into mice intra-peritoneally for extended periods of time (Pamphlett et al. 2000; Stoltenberg et al. 2003). These authors also reported that although mobilization of bismuth from the shot occurred over months, no detrimental effects on weight gain, movements, and appetite were observed. Nevertheless, these authors urged caution concerning uptake of bismuth from embedded shot.
Several shot types approved by the U.S. Fish and Wildlife Service contain varying amounts of nickel, ranging from 2.8%, 5–7%, to up to 40% nickel (Table 1). In theory, animals subject to hunting could carry embedded shot of these types in various regions of their body. Kalinich et al. (2005) demonstrated that muscle-embedded pellets of tungsten alloys containing 6% nickel caused the appearance of fatal tumors in rats within 26–38 weeks of implantation, depending on dose level. Pure nickel control pellet implants caused mortality of all rats within 30 weeks. Given that game birds and mammals would likely retain shot for greater lengths of time, the possibility arises of their generating fatal tumors from tungsten alloy shot containing up to 40% nickel (see Table 1). However, there are no case reports or studies to support this stated possibility in wild birds and mammals. A similar situation is not likely to arise in animals struck by bullets containing nickel because most hits from bullets, if not immediately fatal, would produce death within a much shorter period before signs of tumor development would appear. Thomas (2015b) urged caution in distinguishing tungsten alloys from tungsten metal (elemental W), and tungsten chemical compounds, indicating that the carcinogenic effect is often caused by another metal in the alloy, rather than the metallic tungsten with which it is alloyed (Verma et al. 2011). The issue of embedded shot also includes the element of such shot, if made from a toxic substance, to cause intoxication when the target animal eventually is consumed by predators or scavengers.
Most of the non-lead bullets developed to replace lead are made from pure copper or copper-zinc alloy, with or without other metal jacket coatings (Paulsen et al. 2015; Thomas et al. 2016). Because there is a risk of spent bullets and their fragments being ingested by scavengers from discarded gut piles, non-retrieved killed or wounded animals, and ingestion by humans who consume bullet fragments in meat from game animals, there is need to demonstrate non-toxicity of copper-based bullets to animals. Franson et al. (2012) reported that American kestrels (Falco sparverius) that were dosed experimentally with copper shot exhibited no signs of copper toxicity. Paulsen et al. (2015) simulated the release of different metals from non-lead rifle bullet fragments in game meat during storage and ingestion. The release of copper and zinc from meat posed no toxic risk post-ingestion by humans, but the authors advised that the aluminum, nickel, and lead content of bullets be kept deliberately low. Irschik et al. (2013) indicated that the release of copper from shot game would not contribute much released metal to humans, concluding that the daily recommended daily intake of copper would not be exceeded, especially if bullet fragments around the entry site were removed. However, solid copper bullets do not fragment to the same extent as bonded and unbonded lead-core bullets (Hunt et al. 2009; Irschik et al. 2013; Stokke et al. 2017).
Shot made from 100% zinc3 and 100% copper (including corrosion-inhibited copper), while made and sold in Europe, is not listed in Table 1. Ingested zinc shot are acutely toxic to waterfowl (Levengood et al. 1999, 2000), which precludes their being given approval under US federal legislation. Presumably, discarded small fishing weights made of zinc would be also toxic to waterbirds that might ingest them. Fäth et al. (2018) demonstrated high leaching rates of commercial zinc shot and copper shot in freshwater that rendered the aquatic media toxic to Daphnia magna, and commented on the inadvisability of zinc and copper as lead shot substitutes. Zinc, as gunshot and fishing weights should not be allowed for manufacture and use in any jurisdiction, given its potential toxic risk to animals that might ingest it and to the aquatic environment. Zinc can be alloyed with copper to make brass, which lowers the mobility of zinc in solution. Copper can be alloyed with tin to make bronze which lowers the mobility of copper in acid aqueous media (Thomas et al. 2007; Thomas and McGill 2008). Therefore, brass and bronze, whether used in bullets or fishing weights, exhibit less potential toxicity to animals which might ingest them, or to the freshwater environment where many discarded weights remain.
It is also assumed that shot made from lead with either a thin plastic or other metal coat would not receive approval because such coatings of ingested shot would be removed quickly in avian gizzards, exposing a conventional lead core to the digestive actions of the gut. It matters little whether the shot were picked up from a marsh or ground, or from the bodies of wounded or dead birds in which it was embedded. Attempts to cover lead shot with a protective coating of non-toxic metals or other materials to prevent the degradation and uptake of lead while in the gizzard/stomach of birds have all resulted in failure to prevent lead toxicity (Friend et al. 2009).
Discussion
Thomas and Guitart (2003) proposed an alternative system for evaluating the toxicity of proposed lead substitutes based on the US Fish and Wildlife Service protocol, and which relied on a more rapidly breeding avian test species. In view of the fact that no new candidate substitutes of lead shot have been unconditionally approved since 2006, it appears advisable to proceed with the already-approved list of non-toxic materials (with several considerations) for use in shot, bullets, and fishing weights. These are presented in Table 2.
Table 2.
Metal/metal alloy | Shotgun shot | Rifle bullets or shotgun slugs | Fishing sinkers |
---|---|---|---|
Iron, Fe | ≥ 99% Fe | Not suited | Suitable as corrosion-resistant “stainless” steel for weights and jigs |
Tungsten, W | 95% W, with polymer | Any %W, when used as a densifier with other approved material | Any %W, when mixed with polymers, glass, or other approved material |
Tin, Sn | While demonstrated to be non-toxic, and unconditionally approved in Canada, the low-density limits use as gunshot | Not suited when used alone, but can be used in conjunction with other approved materials | Suitable for use as split shot, weights, or jigs |
Bismuth-tin alloy, Bi-Sn | Suitable and fully approved in USA and Canada | Not suitable, due to frangibility concerns at high-velocity impacts | Suitable as weights and jigs |
Bronze, copper-tin alloy, Cu-Sn | Suitable, especially when used in conjunction with denser tungsten | Potentially suitable, but metal hardness may be problematic | Suitable as weights and jigs |
Copper, Cu | Not suitable, see Fäth et al. (2018) for aquatic environmental concerns | Highly suitable, either as pure Cu, or as a 95% Cu—5% Zn alloy | Suitable as a 95% Cu—5% Zn alloy to resist corrosion |
Lead, Pb | Less than 0.1% by mass | Less than 0.1% by mass | Less than 0.1% by mass |
Zinc, Zn | Less than 1% by mass | Allowed only as an alloying metal | Allowed only as an alloying metal |
Nickel, Ni | Less than 1% by mass | Allowed as a bullet jacket coat | Less than 1% by mass |
Iron in stainless steel is unacceptable, ballistically, because of its greater hardness than annealed iron shot. This would increase pressures beyond safe limits, and be also more expensive to produce
See “Discussion” about high levels of nickel permitted in some types of approved non-toxic gunshot
The importance of Table 2 is that it can be used as the basis of compositional regulations used for shotgun and rifle ammunition and fishing weights, either by a single country or all member nations of the European Union or other international institutions. Listing of ammunition and sinker materials that fulfill basic criteria for non-toxicity would assist the many countries that have yet to make a transition to non-lead recreational products. The US and Canadian regulations are constrained by jurisdictional authority in that they cannot regulate anything under state/provincial authority, including fishing sinkers and hunting rifle bullets. Other countries are free from such constraints, enabling compositional standards to be set across the entire range of these products. This would be the first time that the allowable composition of sinkers and rifle bullets would be defined. Such standards would benefit the makers of ammunition and sinkers, would promote international trade in these non-lead products, and would facilitate enforcement of non-lead regulations and user compliance. Should metals not listed in Table 2 (e.g., cadmium) be made into ammunition or fishing weights, it is advisable that they undergo a toxicological examination similar to that proposed in the US Fish and Wildlife Service regulations (USFWS 1997) prior to sale.
A critical aspect of regulation is that it sets enforceable production standards, ensuring that unwanted contaminants do not enter production. Metals such as bismuth are obtained from other metal refining, and are readily contaminated by lead unless high-grade products are used. Kanstrup (2012) found that bismuth-tin shot contained up to 6,800 ppm (0.68%) lead by mass. Thus, bismuth used in shot making must be initially of high grade. The same comment regarding purity of the metal used for shot making applies to tungsten, which is available as a commercial waste material containing nickel, or as a high-grade refined product. Thus, setting the maximum allowable content of lead, zinc, or nickel at less than 1% is realistic from a production point of view, while ensuring a high level of toxic threat protection to birds that might ingest these products. The permissible lead level in gunshot is 1% for the USA and Canada, but 0.1% for Denmark, consistent with Danish criteria for lead exposure.
Acknowledgements
I am grateful to the reviewers for their constructive comments on this paper. Funding was provided from the personal resources of Vernon G. Thomas.
Vernon G. Thomas
is a Professor Emeritus specializing in the transfer of scientific knowledge to conservation policy and law, especially in the issue of lead exposure and toxicity in wildlife and humans.
Footnotes
The term “fishing weights” includes split shot, sinkers, worm weights, trolling weights, jigheads, and fishing gear or tackle.
Non-lead means, currently, containing less than 1% lead by mass. This term is used synonymously with “lead-free.”
Zinc is a commonly available, inexpensive metal that has a low melting point (419.5 °C), and can be made into shot using similar processes as for lead shot. Its density of 7.14 g/cm3 means that it can be used as a ballistic substitute for lead shot, especially in jurisdictions lacking compositional shot regulations. While zinc shot cartridges are marketed as “lead-free” the implication that they are non-toxic is false.
References
- Arnemo JM, Anderson O, Stokke S, Thomas VG, Krone O, Pain DJ, Mateo R. Health and environmental risks from lead-based ammunition: science versus socio-politics. EcoHealth. 2016;13:618–622. doi: 10.1007/s10393-016-1177-x. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Delahay, R.J. and C.J. Spray (eds.). 2015. Proceedings of the Oxford lead symposium. Lead ammunition: understanding and minimising the risks to human and environmental health. Oxford, UK: Edward Grey Institute, The University of Oxford.
- Falk, K., F. Merkel, K. Kampp, and S.E. Jamieson. 2006. Embedded lead shot and infliction rates in common eiders (Somateria mollissima) and king eiders (S. spectabilis) wintering in southwest Greenland. Wildlife Biology 12: 257–265. 10.2981/0909-6396(2006)12%5b257:elsair%5d2.0.co;2.
- Fäth J, Feiner M, Beggel S, Geist J, Göttlein A. Leaching behavior and ecotoxicological effects of different game shot materials in freshwater. Knowledge and Management of Aquatic Ecosystems. 2018;419:24–31. doi: 10.1051/kmae/2018009. [DOI] [Google Scholar]
- Franson JC, Hansen SP, Creekmore TE, Brand CJ, Evers DC, Duerr AE, DeStefano S. Lead fishing weights and other fishing tackle in selected waterbirds. Waterbirds. 2003;26:345–352. doi: 10.1675/1524-4695(2003)026[0345:LFWAOF]2.0.CO;2. [DOI] [Google Scholar]
- Franson JC, Lahner LL, Meteyer CU, Rattner BA. Copper pellets simulating oral exposure to copper ammunition: absence of toxicity in American kestrels (Falco sparverius) Archives of Contamination and Toxicology. 2012;62:145–153. doi: 10.1007/s00244-011-9671-1. [DOI] [PubMed] [Google Scholar]
- Friend M, J.C. Franson, and W.L.Anderson. 2009. Biological and societal dimensions of lead poisoning of birds in the USA. In Ingestion of lead from spent ammunition: Implications for wildlife and humans. eds. Watson R.T., M. Fuller, M. Pokras, and W.G. Hunt, 34–60. Boise, ID. The Peregrine Fund. 10.4080/ilsa.2009.0104.
- Grade TJ, Pokras MA, Laflamme EA, Vogel HS. Population-level effects of lead fishing tackle on common loons. Journal of Wildlife Management. 2018;82:155–164. doi: 10.1002/jwmg.21348. [DOI] [Google Scholar]
- Hansen E, Lassen C, Elbaek-Jørgensen A. Advantages and drawbacks of restricting the marketing and use of lead in ammunition, fishing sinkers and candle wicks. Brussels: Enterprise Directorate-General, European Commission; 2004. [Google Scholar]
- Hicklin PW, Barrow WR. Incidence of embedded shot in waterfowl in Atlantic Canada and Hudson Strait. Waterbirds. 2004;27:41–45. doi: 10.1675/1524-4695(2004)027[0041:TIOESI]2.0.CO;2. [DOI] [Google Scholar]
- Hunt WG, Watson RT, Oaks JL, Parish CN, Burnham KK, Tucker RL, Belthoff JR, Hart G. Lead bullet fragments in venison from rifle-killed deer: Potential for human dietary exposure. PLoS ONE. 2009;4:e5330. doi: 10.1371/journal.pone.0005330. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Irschik I, Bauer F, Sager M, Paulsen P. Copper residues in meat from wild artiodactyls hunted with two types of rifle bullets manufactured from copper. European Journal of Wildlife Research. 2013;59:129–136. doi: 10.1007/s10344-012-0656-9. [DOI] [Google Scholar]
- Kalinich JF, Emond CA, Dalton TM, Mog SR, Coleman GD, Kordell JE, Miller AC, McClain DE. Embedded weapons-grade tungsten alloy shrapnel induces metastatic high-grade rhabdomyosacomas in F344 rats. Environmental Health Perspectives. 2005;113:729–734. doi: 10.1289/ehp.7791. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Kanstrup, N. 2012. Lead in game birds in Denmark: levels and sources. Danish Academy of Hunting. Article 2012-02-1. http://www.danskjagtakademi.dk/fileadmin/user_upload/NK/120208_Danish_Academy_of_Hunting__1202-01_Lead_in_birds_in_Denmark.pdf.
- Kanstrup N, Swift J, Stroud DA, Lewis M. Hunting with lead ammunition is not sustainable: European perspectives. Ambio. 2018 doi: 10.1007/s13280-018-1042-y. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Kraabel BJ, Miller MW, Getzy DM, Ringelman JK. Effects of embedded tungen-bismuth-tin shot and steel shot on Mallards (Anas platyrhynchos) Journal of Wildlife Diseases. 1996;32:1–8. doi: 10.7589/0090-3558-32.1.1. [DOI] [PubMed] [Google Scholar]
- Levengood JM, Sanderson GC, Anderson WL, Foley GL, Skowron LM, Brown PW, Seets JW. Acute toxicity of ingested zinc shot to game-farm mallards. Illinois Natural History Survey Bulletin. 1999;36:1–36. [Google Scholar]
- Levengood JM, Sanderson GC, Anderson WL, Foley GL, Brown PW, Seets JW. Influence of diet on the hematology and serum biochemistry of zinc-intoxicated mallards. Journal of Wildlife Diseases. 2000;36(1):111–123. doi: 10.7589/0090-3558-36.1.111. [DOI] [PubMed] [Google Scholar]
- Mitchell RR, Fitzgerald SD, Auerlich RJ, Balander RJ, Powell DC, Templeman RJ, Sickle RL, Stevens W, Bursian SJ. Health effects following chronic dosing with tungsten-iron and tungsten-polymer shot in adult-game farm mallards. Journal of Wildlife Diseases. 2001;37:451–458. doi: 10.7589/0090-3558-37.3.451. [DOI] [PubMed] [Google Scholar]
- Mitchell RR, Fitzgerald SD, Auerlich RJ, Balander RJ, Powell DC, Templeman RJ, Cray C, Stevens W, Bursian SJ. Hematological effects and metal residue concentrations following chronic dosing with tungsten-iron and tungsten polymer shot in adult game-farm mallards. Journal of Wildlife Diseases. 2001;37:459–467. doi: 10.7589/0090-3558-37.3.459. [DOI] [PubMed] [Google Scholar]
- Mitchell RR, Fitzgerald SD, Auerlich RJ, Balander RJ, Powell DC, Templeman RJ, Stevens W, Bursian SJ. Reproductive effects and ducking survivability following chronic dosing with tungsten-iron and tungsten-polymer shot in game-farm mallards. Journal of Wildlife Diseases. 2001;37:468–474. doi: 10.7589/0090-3558-37.3.468. [DOI] [PubMed] [Google Scholar]
- Norton MR, Thomas VG. Economic analyses of crippling losses of North American waterfowl and their policy implications for management. Environmental Conservation. 1994;21:347–353. doi: 10.1017/S037689290003366X. [DOI] [Google Scholar]
- Pamphlett R, Dancher G, Rungby J, Stoltenberg M. Tissue uptake of bismuth from shotgun pellets. Environmental Research Section A. 2000;82:258–262. doi: 10.1006/enrs.1999.4016. [DOI] [PubMed] [Google Scholar]
- Paulsen P, Bauer F, Sager M, Schumann-Irschik I. Model studies for the release of metals from embedded rifle bullet fragments during simulated meat storage and food ingestion. European Journal of Wildlife Research. 2015;61:629–633. doi: 10.1007/s10344-015-0926-4. [DOI] [Google Scholar]
- Sanderson GC, Anderson WL, Foley GL, Duncan KL, Skowron LM, Brawn JD, Seets JW. Toxicity of ingested bismuth alloy shot in game farm mallards: chronic health effects on reproduction. Illinois Natural History Survey Bulletin. 1997;35:217–252. [Google Scholar]
- Sanderson GC, Anderson WL, Foley GL, Havera SP, Skowron LM, Brawn JW, Taylor GD, Seets JW. Effects of lead, iron, and bismuth alloy shot embedded in the breast muscle of game-farm mallards. Journal of Wildlife Diseases. 1998;34:688–697. doi: 10.7589/0090-3558-34.4.688. [DOI] [PubMed] [Google Scholar]
- SEAC (Committee for Socio-Economic Analysis). 2018. Lead gunshot restriction in wetlands. https://echa.europa.eu/-/rac-adopts-13-proposals-for-harmonised-classification-and-labelling-and-seac-adopts-the-restriction-proposal-on-lead-in-gunshot.
- Stokke S, Brainerd S, Arnemo JM. Metal deposition of copper and lead bullets in moose harvested in Fennoscandia. Wildlife Society Bulletin. 2017;41(1):98–106. doi: 10.1002/wsb.731. [DOI] [Google Scholar]
- Stoltenberg M, Locht L, Larsen A, Jensen D, Danscher G. In vivo cellular uptake of bismuth ions from shotgun pellets. Histology and Histopathology. 2003;18:781–785. doi: 10.14670/HH-18.781. [DOI] [PubMed] [Google Scholar]
- Stroud, D.A. 2015. Regulation of some sources of lead poisoning: a brief review. In Proceedings of the Oxford Lead Symposium. Lead ammunition: understanding and minimising the risks to human and environmental health. eds. Delahay, R.J. and C.J. Spray, 8–26. Oxford, UK: Edward Grey Institute, The University of Oxford.
- Thomas, V.G. 2015a. Availability and use of lead-free shotgun and rifle cartridges in the UK, with reference to regulations in other jurisdictions. In Proceedings of the Oxford Lead Symposium. Lead ammunition: understanding and minimising the risks to human and environmental health. eds. Delahay, R.J. and C.J. Spray, 85–97. Oxford, UK: Edward Grey Institute, The University of Oxford.
- Thomas VG. Elemental tungsten, tungsten-nickel alloys and shotgun ammunition: resolving issues of their relative toxicity. European Journal of Wildlife Research. 2015;62:1–9. doi: 10.1007/s10344-015-0979-4. [DOI] [Google Scholar]
- Thomas VG, Guitart R. Evaluating non-toxic substitutes for lead shot and fishing weights: Criteria and regulations. Environmental Policy and Law. 2003;33(3–4):143–149. [Google Scholar]
- Thomas VG, McGill IR. Dissolution of copper, tin, and iron from sintered tungsten-bronze spheres in a simulated avian gizzard, and an assessment of their potential toxicity to birds. Science of the Total Environment. 2008;394:283–289. doi: 10.1016/j.scitotenv.2008.01.049. [DOI] [PubMed] [Google Scholar]
- Thomas VG, Santore RV, McGill I. Release of copper from sintered tungsten-bronze shot under different pH conditions and its potential toxicity to aquatic organisms. Science of the Total Environment. 2007;374:71–79. doi: 10.1016/j.scitotenv.2006.10.004. [DOI] [PubMed] [Google Scholar]
- Thomas VG, Roberts MJ, Harrison PTC. Assessment of the environmental toxicity and carcinogenicity of tungsten-based shot. Ecotoxicology and Environmental Safety. 2009;72:1031–1037. doi: 10.1016/j.ecoenv.2009.01.001. [DOI] [PubMed] [Google Scholar]
- Thomas VG, Gremse C, Kanstrup N. Non-lead rifle hunting ammunition: Issues of availability and performance in Europe. European Journal of Wildlife Research. 2016;62(6):633–641. doi: 10.1007/s10344-016-1044-7. [DOI] [Google Scholar]
- USFWS (US Fish and Wildlife Service) Migratory bird hunting: Revised test protocol for nontoxic approval procedures for shot and shot coating; final rule. Federal Register. 1997;62(230):63607–63615. [Google Scholar]
- USFWS (US Fish and Wildlife Service) Migratory bird hunting approval of tungsten-iron-copper-nickel, iron-tungsten-nickel alloy, tungsten-bronze (additional information), and tungsten-iron-tin shot types as non-toxic for hunting waterfowl and coots: Availability of environmental assessments. Federal Register. 2006;71(17):4294–4297. [Google Scholar]
- USFWS (US Fish and Wildlife Service) Migratory bird hunting: Revision of language for approval of nontoxic shot for use in waterfowl hunting. Federal Register. 2013;78(248):78275–78284. [Google Scholar]
- Verma R, Xu X, Jaiswal MJ, Olsen C, Mears D, Caretti G, Galdzicki Z. In vitro profiling of epigenetic modifications underlying heavy metal toxicity of tungsten-alloy and its components. Toxicology and Applied Pharmacology. 2011;253:178–187. doi: 10.1016/j.taap.2011.04.002. [DOI] [PubMed] [Google Scholar]
- Watson RT, Fuller M, Pokras M, Hunt WG, editors. Ingestion of lead from spent ammunition: Implications for wildlife and humans. Boise, ID: The Peregrine Fund; 2009. [Google Scholar]