Source: CORNELL UNIVERSITY submitted to NRP
LEAD LOSS FROM BLOOD AND MILK AND THE LEVEL OF CONTAMINATION OF MUSCLE, LIVER, KIDNEY, AND BONE IN LEAD EXPOSED CATTLE
Sponsoring Institution
National Institute of Food and Agriculture
Project Status
COMPLETE
Funding Source
Reporting Frequency
Annual
Accession No.
0209181
Grant No.
(N/A)
Cumulative Award Amt.
(N/A)
Proposal No.
(N/A)
Multistate No.
(N/A)
Project Start Date
Oct 1, 2006
Project End Date
Sep 30, 2009
Grant Year
(N/A)
Program Code
[(N/A)]- (N/A)
Recipient Organization
CORNELL UNIVERSITY
(N/A)
ITHACA,NY 14853
Performing Department
VET POPULATION MEDICINE & DIAGNOSTIC SCIENCE
Non Technical Summary
Lead poisoning in cattle is a common problem and could cause to lead contamination milk or meat entering the human food chain. This study will determine the rate of lead loss from exposed cattle and the best way to manage exposed cattle to prevent contamination of cow milk and beef intended for human consumption.
Animal Health Component
50%
Research Effort Categories
Basic
50%
Applied
50%
Developmental
(N/A)
Classification

Knowledge Area (KA)Subject of Investigation (SOI)Field of Science (FOS)Percent
3143399115035%
3143499115035%
7113399115015%
7113499115015%
Goals / Objectives
1. This study will characterize lead contamination in animals with clinical lead poisoning and those with no clinical signs of poisoning in herds with known exposure to lead. We will determine the source of the lead and the importance of lead contamination in asymptomatic animals from such herds. We will use blood analysis and milk analysis from live animals and tissue analysis including liver, muscle, and bone from dead animals. 2. We will determine the rate of lead elimination over time based on the decrease in blood and milk lead concentrations. Blood represents the circulating lead that is not stored in tissues. Blood is easily collected and is frequently used to monitor the level of exposure and response to treatment in animals exposed to lead. Milk is a potential route of lead excretion and preliminary results show elevated lead concentrations in milk from exposed animals. Milk is chosen for analysis because it is easily collected from most lactating cows and is a human food. Knowledge of the rate of lead loss from blood and milk will help the veterinary diagnostic community to estimate when lead exposed cattle can be safely returned to food production. 3. We will also determine the level of lead contamination in solid animal products such as muscle and organ meat (liver and kidney) that are sources of food for humans. This information will be used to assess the safety of the meat produced and the additional economic impact of lead poisoning. Lead concentrations in bone will be determined because bone is a major storage site for lead. Lead can be released from bone over the lifetime of the animal, particularly during growth (Rumbeiha et al. 2001) and at parturition (Waldner et al. 2002, Galey et al. 1990). Small amounts of lead sometimes leach from bone during food preparation (Baxter et al. 1992) 4. We will use field cases of lead exposure. The data generated will be immediately applicable to the control of lead poisoning and lead contamination of animals in field cases. The information accumulated will be easily applicable to future field cases of lead poisoning. 5. We will publish our results in a peer-reviewed journal.
Project Methods
1. Six herds will be invited to participate. Participation will be anonymous. Compensation will be available to participating veterinarians. The New York Department of Agriculture and Markets will encourage participation. If we are unable to locate 2 herds within the first year, herds identified by other laboratories will be invited. 2. We estimate that 10-30 animals per herd will be sampled based on our experience with small herds of 20-80 animals and limited lead exposure within herds. a. Environmental samples will be collected to determine the source of lead. The Analytical Toxicology Laboratory at the Animal Health Diagnostic Center (AHDC) routinely processes samples for quantitative lead analysis using atomic absorption spectroscopy (AA). b. Blood and milk will be collected to determine the level of exposure of symptomatic and asymptomatic exposed cattle. Blood samples will be collected from beef calves and dams. Milk and blood will be collected from lactating cows when possible. c. Tissue samples (muscle, liver, kidney, bone) will be collected from cattle that die, are culled, or are slaughtered. We expect to collect tissues from 12 cattle and that 6 of these will transported to the AHDC for routine necropsy. 2. The rate of elimination is expected to follow first-order kinetics, (i.e., half the dose is eliminated per unit time) so the absolute amount eliminated will decrease with time. Sampling will be repeated at increasing intervals: 2 weeks (1st interval), 4 weeks (2nd interval), and 8-12 weeks (3rd interval to end) and terminated at lead concentrations of 2.5 micrograms per deciliter. a. Samples will be analyzed routinely at AHDC. b. The half-life of lead in blood will be calculated using the equation half-life = 0.693/slope. Slope is calculated from a computer-generated semilog plot of the change in concentration over time (Rumbeiha et al, 2001). c. We will determine if the equation log(y) = 3.19(x)-2.36, where y is the concentration of lead in milk and x is the concentration in blood, (Oskarsson et al. 1992) describes our findings. 3. Muscle, liver, kidney, and bone will be collected from cattle removed from the study due to death or culling. Bone will be collected from the distal physis of the femur where a change in bone density was seen in a lead poisoned calf (OConnor and Doige 1993). Adjacent gastrocnemius muscle will be collected. Lead concentrations are highest in muscle less than 10 millimeters from bone (Baxter et al., 1992). Rumen contents and abomasal contents will be collected to rule out continued exposure. Complete necropsies will be performed on carcasses that can be moved to the AHDC (est. 6). Field collection will be performed on other carcasses with samples collected for routine histopathology. Samples for lead analysis will be processed routinely at AHDC. 4. Collected data will be reported to the herd veterinarian. The source of lead will be removed from the environment of the animals as soon as possible. 5. We will publish the results of this study in the form of one or more manuscripts in peer-reviewed journals such as the Journal of Veterinary Diagnostic Investigation.

Progress 10/01/06 to 09/30/09

Outputs
OUTPUTS: 30 head of cattle from herds with known lead exposure were added to this study from 4 different farms. Approximately 75 blood samples were collected from these cattle. 34 urine samples were collected from 16 cows on one farm. Numerous environmental samples were analyzed to determine the source of lead contamination on the farms. Additionally, carcasses of 2 euthanized cattle were purchased and complete necropsy and tissue collection was done. A total of 224 cattle from 7 farms have been sampled for this 3-year study. Samples have included blood, urine, and milk. PARTICIPANTS: Karyn Bischoff was the principle investigator. She is director of the analytical toxicology laboratory, where samples were analyzed. She has collected the data in spreadsheets and will continue to process it. She also coordinated local veterinarians who were involved in lead poisoning cases with local herds for sample collection. She was also involved in collection of environmental samples and assisted in collecting biological samples. Belinda Thompson was involved in communication with local veterinarians concerning cases of lead poisoning. As a veterinarian, she collected blood samples and other biological samples from affected cattle herds. William Higgins acted as liason with a large dairy cow herd in Maryland with a history of lead poisoning. Cynthia Gaskill acted as liason with a large herd in Kentucky. She analyzed blood samples for lead in her laboratory to compare lead analysis techniques with our laboratory. TARGET AUDIENCES: The target audiences for this study are cattle producers, veterinarians, and state regulators. Information from herds studied in Maryland and New York has been submitted to state Agriculture Departments and used to promote regulation of meat and milk from animals exposed to lead on the farm. Results from this study have lead to policy changes within these states. Information from this study has also been presented as a poster in a national "One Health" conference to show the importance of animals as sentinels for lead poisoning (Milstein Science Symposium. American Museum of Natural History, New York, NY). PROJECT MODIFICATIONS: The only major change was the collection and submission of blood samples from several farm animals (horses, cat, dog, goat) from a farm with known exposure in cattle. Since the other animals on the farm had similar exposure, and the owner of the farm also had an elevated blood lead concentration, the owner had blood collected from other farm animals for analysis. Blood lead concentrations were elevated in the cat and dog. This information has been accepted for publication.

Impacts
Analysis continues on the data collected. The blood half-life for lead in the cattle in this study ranged from less than 1 to 293 days. The half-life in milk ranged from 44 to 106 days, though excretion through milk was not consistent and would increase in some cows, most likely due to freshening. Urinary lead was only documented in one of the 16 cows for which urine samples were available. Analysis of tissues from 2 cattle with previous lead exposure that would have been deemed appropriate for human consumption with blood lead concentrations that had decreased below 5 micrograms/dL, revealed trace lead concentrations in edible tissues. The highest lead concentration detected in edible tissues was 7ppm (dry matter) detected in gastrocnemius muscle that was directly adjacent to bone. Other edible tissues contained less than 2 ppm lead (dry matter). Findings on cattle in these farms have been reported to veterinarians in the state in which the farms are located. Based on these findings, milk concentrations greater than 10 ppb are not acceptable for human food in the state of Maryland (based on individual cows, not bulk-tank samples). Cows with blood lead concentrations greater than 5 micrograms/dL are not acceptable for slaughter for human consumption in the state of New York. Lead poisoning in food animals is now reportable to the Department of Agriculture and Markets in the state of New York. These changes are intended to protect the human food supply. We were also able to compare our technique for blood lead analysis, AA, with two other techniques, ICP analysis and LeadCare(R) analysis. Information generated from the ICP to AA comparison will be used internally within the analytical toxicology laboratory for test validation and verification purposes. A paper on the comparison of AA and LeadCare(R) analysis has been submitted for publication. There was one farm where lead poisoning was diagnosed in the cattle and later diagnosed in other animals on the farm and the farm owner. The source of lead was paint in the barn and the farm house. This is the first known case where cattle acted as sentinels for lead poisoning in a human.

Publications

  • Animals as sentinels in lead poisoning: 2 case reports. Poster presentation, April 2 & 3, 2009, Milstein Science Symposium. American Museum of Natural History, New York, NY.
  • Bischoff K., Priest H*, Mount-Long A., Animals as sentinels in lead poisoning: a case report. Accepted by J Med Toxicol 2009.


Progress 10/01/07 to 09/30/08

Outputs
OUTPUTS: We have continued to follow up on milk lead concentrations in cattle from the large farm in Maryland. Milk samples have been collected from approximately 130 cow over a period of 3 years since lead poisoning was first documented in the herd. All milk samples tested in 2008 had lead concentrations below the FDA tolerance limit of 10 ppb. We continue to follow blood lead concentrations in cattle on small farms in New York and New Hampshire. We have collaborated with a researcher at the Livestock Disease Diagnostic Center in Lexington, Kentucky to compare routine blood lead testing methods used in our lab, atomic absorption and inductively-coupled plasma-axial emissions spectrophotometry, with a rapid blood lead analysis kit for use in cattle. We tested 57 cattle from a herd with documented lead poisoning. PARTICIPANTS: Karyn Bischoff has formed a collaboration with Dr Gaskill of the Livestock Disease Diagnostic Center in Lexington, KY to develop a rapid screen for lead poisoning in cattle. TARGET AUDIENCES: Nothing significant to report during this reporting period. PROJECT MODIFICATIONS: Nothing significant to report during this reporting period.

Impacts
We have found that 2 years after exposure to lead shot in the diet, milk lead concentrations were below the FDA limit of 10 ppb, which will have implications for future cases of lead poisoning affecting dairy cattle. Our current data also suggests that lead excretion via the milk varies with the stage of lactation. A manuscript has been prepared documenting lead poisoning one one of the farms in this study. This paper describes the use of cattle as sentinels for human lead exposure on a farm. It will be submitted for publication this year. Methods comparison data has been accumulated with help of the Livestock Disease Diagnostic Center in Lexington Kentucky and is awaiting analysis and eventual publication.

Publications

  • No publications reported this period


Progress 10/01/06 to 09/30/07

Outputs
Milk samples were collected seven times during the period from October 2006 through September 2007 from a herd in Maryland. Lead poisoning was documented in this herd in September, 2005. Approximately 35 cows were sampled during this period and 78 total milk samples were analyze and 31 contained concentrations of lead greater than 10ppb. Milk lead concentrations varied from sample to sample, sometimes increasing. Two more farms were added to the study, including one in the state of New York involving 3 surviving dairy calves and another in New Hampshire involving 4 dairy heifers. Forty to 50 environmental and necropsy samples, including tissues, were collected from this herd and are pending analysis.

Impacts
Early collection from the NH herd has indicated a shorter blood half-life for lead in this herd versus previous herds sampled. This could be indicative of the form of lead leading to rapid absorption(ash versus paint and shot in the previous NY herd and MD herd) or a biphasic half-life. Serial milk collections from the MD herd show that a simple half-life cannot be calculated and lead concentrations in milk concentrations may increase and decrease over time. This is most likely due to stage of lactation, as increased bone resorption for to produce calcium is likely to increase the bioavailability of lead. All results have been made available to the referring veterinarian for use in assessment and treatment of animals.

Publications

  • No publications reported this period