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Lead

Sediment

Lead (mg/kg dry weight)

Mussels

Lead (mg/kg wet weight)
North
3.71 mg/kg
3.71 mg/kg
Metlakatla
0.034 mg/kg
0.034 mg/kg
652 mg/kg
652 mg/kg
Prince Rupert
0.432 mg/kg
0.432 mg/kg
2.57 mg/kg
2.57 mg/kg
Wiah Point
0.0439 mg/kg
0.0439 mg/kg
4 mg/kg
4 mg/kg
Armentieres Channel
0.0245 mg/kg
0.0245 mg/kg
3.59 mg/kg
3.59 mg/kg
Bischof Islands
0.0155 mg/kg
0.0155 mg/kg
2.76 mg/kg
2.76 mg/kg
Haswell Bay
0.0186 mg/kg
0.0186 mg/kg
3.76 mg/kg
3.76 mg/kg
Louscoone Inlet
0.0146 mg/kg
0.0146 mg/kg
1.09 mg/kg
1.09 mg/kg
Bella Bella
0.0138 mg/kg
0.0138 mg/kg
2.8 mg/kg
2.8 mg/kg
Port Neville
0.0463 mg/kg
0.0463 mg/kg
7.7 mg/kg
7.7 mg/kg
Sechelt
Not sampled
28.4 mg/kg
28.4 mg/kg
Strait of Georgia 1
Not sampled
31.4 mg/kg
31.4 mg/kg
Strait of Georgia 2
Not sampled
16.15 mg/kg
16.15 mg/kg
Howe Sound 1
Not sampled
4.89 mg/kg
4.89 mg/kg
Howe Sound 2
0.0401 mg/kg
0.0401 mg/kg
17.8 mg/kg
17.8 mg/kg
Howe Sound 3
0.0578 mg/kg
0.0578 mg/kg
12.1 mg/kg
12.1 mg/kg
Indian Arm 1
0.0774 mg/kg
0.0774 mg/kg
5.7 mg/kg
5.7 mg/kg
Indian Arm 2
0.141 mg/kg
0.141 mg/kg
54 mg/kg
54 mg/kg
Burrard Inlet 1
0.143 mg/kg
0.143 mg/kg
23 mg/kg
23 mg/kg
Burrard Inlet 2
Not sampled
5.68 mg/kg
5.68 mg/kg
Burrard Inlet 3
0.147 mg/kg
0.147 mg/kg
6.76 mg/kg
6.76 mg/kg
Burrard Inlet 4
0.137 mg/kg
0.137 mg/kg
28.2 mg/kg
28.2 mg/kg
Burrard Inlet 5
Not sampled
14.4 mg/kg
14.4 mg/kg
Burrard Inlet 6
0.0975 mg/kg
0.0975 mg/kg
20.8 mg/kg
20.8 mg/kg
Burrard Inlet 7
Not sampled
21.2 mg/kg
21.2 mg/kg
Burrard Inlet 8
0.08035 mg/kg
0.08035 mg/kg
Not sampled
Burrard Inlet 9
0.099 mg/kg
0.099 mg/kg
21.55 mg/kg
21.55 mg/kg
Burrard Inlet 10
0.128 mg/kg
0.128 mg/kg
17.3 mg/kg
17.3 mg/kg
Burrard Inlet 11
Not sampled
17 mg/kg
17 mg/kg
Burrard Inlet 12
Not sampled
16.1 mg/kg
16.1 mg/kg
Burrard Inlet 13
Not sampled
14.8 mg/kg
14.8 mg/kg
Burrard Inlet 14
Not sampled
Not sampled
Burrard Inlet 15
0.115 mg/kg
0.115 mg/kg
3.34 mg/kg
3.34 mg/kg
Fraser River 1
0.065 mg/kg
0.065 mg/kg
16.5 mg/kg
16.5 mg/kg
Fraser River 2
Not sampled
16.4 mg/kg
16.4 mg/kg
Fraser River 3
Not sampled
Not analyzed
Fraser River 4
Not sampled
Not analyzed
Fraser River 5
Not sampled
Not sampled
Fraser River 6
0.0989 mg/kg
0.0989 mg/kg
Not sampled
Fraser River 7
0.102 mg/kg
0.102 mg/kg
3.42 mg/kg
3.42 mg/kg
Tsawwassen
Not sampled
1.18 mg/kg
1.18 mg/kg
Lemmens inlet
Not sampled
1.53 mg/kg
1.53 mg/kg
Grice Bay
Not sampled
4.21 mg/kg
4.21 mg/kg
Dixon Island
0.0326 mg/kg
0.0326 mg/kg
4.08 mg/kg
4.08 mg/kg
Saturna Island
0.0571 mg/kg
0.0571 mg/kg
5.66 mg/kg
5.66 mg/kg
Fulford Harbour 1
0.0452 mg/kg
0.0452 mg/kg
3.47 mg/kg
3.47 mg/kg
Fulford Harbour 2
0.0628 mg/kg
0.0628 mg/kg
2.3 mg/kg
2.3 mg/kg
Patricia Bay
0.0522 mg/kg
0.0522 mg/kg
6.85 mg/kg
6.85 mg/kg
Finnerty Cove 1
Not analyzed
3.62 mg/kg
3.62 mg/kg
Finnerty Cove 2
Not sampled
156 mg/kg
156 mg/kg
Victoria Harbour 1
Not sampled
140 mg/kg
140 mg/kg
Victoria Harbour 2
1.27 mg/kg
1.27 mg/kg
152 mg/kg
152 mg/kg
Victoria Harbour 3
Not sampled
77.1 mg/kg
77.1 mg/kg
Victoria Harbour 4
1.03 mg/kg
1.03 mg/kg
8.41 mg/kg
8.41 mg/kg
Albert Head 1
0.11 mg/kg
0.11 mg/kg
7.38 mg/kg
7.38 mg/kg
Albert Head 2
Not sampled
South

What is it?

Lead occurs naturally in the environment as a trace element, and major natural sources include volcanoes and weathering of rocks. Human activities, including mining, smelting, coal combustion, and waste incineration, have greatly increased the distribution and abundance of lead in the environment.1 Lead is also used in the production of batteries, dyes, paints, and metal alloys. Its properties (including high density, low melting point, malleability, and corrosion resistance) have made lead the primary metal used to manufacture ammunition and fishing weights.1

 

How does it get into the ocean?

Lead can enter the marine environment through effluent from large-scale mining and lead smelting activities.1 The long range atmospheric transport of lead can also result in its deposition in the marine environment.2 When lead enters aquatic systems, it is deposited in sediments in association with particulate matter; therefore, sediments act as an important exposure route for marine organisms.3

For both aquatic and terrestrial bird species in particular, the most important exposure route appears to be spent ammunition and lost fishing tackle. Direct exposure occurs via the consumption of lead or lead-contaminated objects, while indirect exposure occurs when predators and scavengers eat animals that were shot with lead ammunition or that ingested lead fishing tackle.1,4

Is it a problem?

Human exposure to lead results largely from environmental sources such as lead-based paints and contaminated dusts and soils.5 There is no ‘safe’ level of lead exposure in humans.In human adults, lead exposure can cause dysfunction in the cardiovascular, reproductive, renal, and central nervous systems.7 It is classified as a probable human carcinogen by the International Agency for Research on Cancer (IARC). In children, lead exposure can cause IQ deficits, ADHD, behavioural challenges, impaired dental health, and delayed sexual maturation.7

Most of the research on lead toxicity in wildlife has been done on birds. Lead poisoning can result in toxicity to kidneys, bones, and the neurological, reproductive, and central nervous systems.1 Specific symptoms include lethargy, anorexia, breast-muscle atrophy, loss of strength and coordination, drooping wings, and changes in vocalization.1

On Midway Atoll in the Pacific Ocean, a decommissioned military base is a significant source of lead in the form of lead-based paint. The ingestion of lead-based paint chips by Laysan albatross chicks resulted in ‘droopwing’ (a symptom of neurotoxicity) and mortality.5

There is much less information regarding the toxicity of lead to marine mammals. In one example, a stranded female harbour seal died despite rehabilitation attempts. A necropsy revealed a lead fishing sinker in her stomach, and changes to the brain, heart, kidney, liver, lymph nodes, and spleen indicated acute lead toxicosis. This was the first documented case of lead toxicosis in a wild marine mammal.8

FACT: The first documented case of lead toxicosis in a wild marine mammal occurred in northern California in 2004. An adult harbour seal died after ingesting a lead fishing sinker.8

Wildlife exposed to lead can also experience toxicity to the immune and neurological systems without showing any obvious signs of dysfunction. In one study, herring gull hatchlings experienced neurological toxicity resulting from lead exposure during early development, and the authors suggested that these impairments may compromise the ability of chicks to survive in the wild.9

What is being done?

The use of lead in products, including paint and gasoline, has been banned in many countries, including Canada and the United States.10,11 Many countries, including Canada, have banned the use of lead shot for waterfowl hunting.12 However, only Sweden and Denmark have banned lead ammunition for all forms of hunting. Denmark has also banned all lead fishing tackle (as of 2002), and lead tackle has been banned in the United Kingdom since 1987. In Canada, it is illegal to use lead fishing tackle weighing less than 50 grams in National Parks and National Wildlife Areas.1 In the United States, individual parks and refuges make decisions about the use of lead fishing gear.

Canadian sediment quality guidelines for lead protective of marine aquatic life are available. However, sediment quality guidelines are derived from toxicity endpoints in benthic invertebrates and are not protective of birds and marine mammals.

What can we do?

As individuals and organizations, we can:

  • Learn more about lead and other toxic metals using the resource links below
  • Recycle and dispose of waste responsibly and according to local guidelines

More Information?

1 Haig SM, D’Elia J, Eagles-Smith C, Fair JM, Gervais J, Herring G, Rivers JW, Schulz JH. 2014. The persistent problem of lead poisoning in birds from ammunition and fishing tackle. The Condor 116: 408-428.

2 NCM 2003. Lead Review.  Nordic Council of Ministers, January 2003. Report No. 1, Issue No. 4. 31 pp.

3 Eisler, R. 1988. Lead hazards to fish, wildlife, and invertebrates a synoptic review. U.S. Fish and Wildlife Service Biological Report 85(1.14) 134 pp.

4 Finkelstein ME, Doak, DF, George D, Burnett J, Brandt J, Church M, Grantham J, Smith DR. 2012. Lead poisoning and the deceptive recovery of the critically endangered California condor. Proceedings of the National Academy of Sciences 109: 11449-11454.

5 Finkelstein ME, Gwiazda RH, Smith DR. 2003. Lead poisoning of seabirds: Environmental risks from leaded paint at a decommissioned military base. Environmental Science and Technology 37: 3256-3260.

6 CDC. 2012. Low Level Lead Exposure Harms Children: A Renewed Call for Primary Prevention. January 4, 2012. Report of the Advisory Committee on Childhood Lead Poisoning Prevention of the Centers for Disease Control and Prevention.  Available at: http://www.cdc.gov/nceh/lead/ACCLPP/Final_Document_030712.pdf

7 Bellinger, DC. 2011. The protean toxicities of lead: New chapters in a familiar story. International Journal of Environmental Research and Public Health 8: 2593-2628.

8 Zabka TS, Haulena M, Puschner B, Gulland FMD, Conrad PA, Lowenstine LJ. 2006. Acute lead toxicosis in a harbor seal (Phoca vitulina richardsi) consequent to ingestion of a lead fishing sinker. Journal of Wildlife Diseases 42: 651-657.

9 Dey PM, Burger J, Gochfeld M, Reuhl KR. 2000. Developmental lead exposure disturbs expression of synaptic neural cell adhesion molecules in herring gull brains. Toxicology 146: 137-147.

10 ECCC. 2014. Lead. Environment and Climate Change Canada Fact Sheet. Available at: https://www.canada.ca/en/health-canada/services/chemical-substances/fact-sheets/chemicals-glance/lead.html

11 USGS 2009. Lead poisoning in wild birds. United States Geological Survey National Wildlife Health Center Fact Sheet 2009-3051.

12 Clark AJ, Scheuhammer AM. 2003. Lead poisoning in upland-foraging birds of prey in Canada. Ecotoxicology 12 (1-4): 23-30.

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