Bovine Spongiform Encephalopathy; Minimal-Risk Regions; Importation of Live Bovines and Products Derived From Bovines, 53314-53379 [07-4595]
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Federal Register / Vol. 72, No. 180 / Tuesday, September 18, 2007 / Rules and Regulations
Unit 43, Riverdale, MD 20737–1231;
(301) 734–6954.
SUPPLEMENTARY INFORMATION:
DEPARTMENT OF AGRICULTURE
Animal and Plant Health Inspection
Service
9 CFR Parts 93, 94, 95, and 96
[Docket No. APHIS–2006–0041]
RIN 0579–AC01
Bovine Spongiform Encephalopathy;
Minimal-Risk Regions; Importation of
Live Bovines and Products Derived
From Bovines
Animal and Plant Health
Inspection Service, USDA.
ACTION: Final rule.
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AGENCY:
SUMMARY: We are amending the
regulations regarding the importation of
animals and animal products to
establish conditions for the importation
of the following commodities from
regions that present a minimal risk of
introducing bovine spongiform
encephalopathy into the United States:
Live bovines for any use born on or after
a date determined by the Animal and
Plant Health Inspection Service to be
the date of effective enforcement of a
ruminant-to-ruminant feed ban in the
region of export; blood and blood
products derived from bovines; and
casings and part of the small intestine
derived from bovines. We are making
these amendments after conducting a
risk assessment and comprehensive
evaluation of the issues and concluding
that such bovines and bovine products
can be safely imported under the
conditions described in this rule. This
document also removes the delay in
applicability of certain provisions of a
final rule published in January 2005.
DATES: Effective Date: November 19,
2007.
FOR FURTHER INFORMATION CONTACT: For
information regarding ruminant
products, contact Dr. Karen JamesPreston, Director, Technical Trade
Services, Animal Products, National
Center for Import and Export, VS,
APHIS, 4700 River Road Unit 38,
Riverdale, MD 20737–1231; (301) 734–
4356.
For information concerning live
ruminants, contact Dr. Lee Ann Thomas,
Director, Technical Trade Services,
Animals, Organisms and Vectors, and
Select Agents, National Center for
Import and Export, VS, APHIS, 4700
River Road Unit 38, Riverdale, MD
20737–1231; (301) 734–4935.
For other information concerning this
proposed rule, contact Dr. Lisa
Ferguson, Senior Staff Veterinarian,
National Center for Animal Health
Programs, VS, APHIS, 4700 River Road
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Purpose
This document makes final a
proposed rule that the Animal and Plant
Health Inspection Service (APHIS) of
the U.S. Department of Agriculture
(USDA or the Department) published in
the Federal Register on January 9, 2007
(72 FR 1101–1129, Docket No. APHIS–
2006–0041). Additionally, it removes
the delay of applicability of certain
provisions of a final rule APHIS
published in January 2005. The removal
of delay is discussed below under the
heading ‘‘Removal of Partial Delay of
Applicability of Provisions of January
2005 Final Rule.’’
In our January 2007 proposed rule, we
proposed to amend the regulations in 9
CFR parts 93, 94, 95, and 96 to establish
conditions for the importation of the
following commodities from regions
that present a minimal risk of
introducing bovine spongiform
encephalopathy (BSE) into the United
States: Live bovines for any use born on
or after a date determined by APHIS to
be the date of effective enforcement of
a ruminant-to-ruminant feed ban in the
region of export; blood and blood
products derived from bovines; and
casings and part of the small intestine
derived from bovines.
In this document, we respond to
public comments received on the
proposed rule and its underlying risk
assessment and other supporting
analyses. Additionally, we discuss
below the history of APHIS rulemaking
related to BSE minimal-risk regions.
Background
APHIS regulates the importation of
animals and animal products into the
United States to guard against the
introduction of animal diseases. The
regulations in 9 CFR parts 93, 94, 95,
and 96 (referred to below as the
regulations) govern the importation of
certain animals, birds, poultry, meat,
other animal products and byproducts,
hay, and straw into the United States in
order to prevent the introduction of
various animal diseases, including BSE,
a chronic degenerative disease affecting
the central nervous system of cattle.
With some exceptions, APHIS’
regulations prohibit or restrict the
importation of live ruminants and
certain ruminant products and
byproducts from the following three
categories of regions with regard to BSE:
(1) Those regions in which BSE is
known to exist (listed in § 94.18(a)(1) of
the regulations); (2) those regions that
present an undue risk of introducing
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BSE into the United States because their
import requirements are less restrictive
than those that would be acceptable for
import into the United States and/or
because the regions have inadequate
surveillance (listed in § 94.18(a)(2) of
the regulations); and (3) those regions
that present a minimal risk of
introducing BSE into the United States
via live ruminants and ruminant
products and byproducts (listed in
§ 94.18(a)(3) of the regulations).
Chronology of Federal Register
Publications Regarding BSE MinimalRisk Regions
We added the § 94.18(a)(3) category
(BSE minimal-risk regions) to the
regulations in a final rule published in
the Federal Register on January 4, 2005
(70 FR 459–553, Docket No. 03–080–3).
In the final rule, we specified which
commodities may be imported from BSE
minimal-risk regions and under what
conditions, and recognized Canada as a
BSE minimal-risk region. (At this time,
Canada is the only recognized BSE
minimal-risk region.)
The January 2005 final rule was based
on a proposed rule we published in the
Federal Register on November 4, 2003
(68 FR 62386–62405, Docket No. 03–
080–1). On December 25, 2003, less than
2 weeks before the close of the comment
period for our proposed rule, a case of
BSE in a dairy cow of Canadian origin
in Washington State was verified by an
international reference laboratory.
In response to comments from the
public requesting an extension of the
comment period and in order to give the
public an additional opportunity to
comment on the proposed rule in light
of this development, on March 8, 2004,
we published a document in the Federal
Register (69 FR 10633–10636, Docket
No. 03–080–2) reopening the comment
period.
On January 4, 2005, along with the
final rule, we published in the Federal
Register a notice (70 FR 554, Docket No.
03–080–4) announcing the availability
of, and requesting comments on, a final
environmental assessment (EA)
regarding the potential impact on the
quality of the human environment due
to the importation of ruminants and
ruminant products and byproducts from
Canada under the conditions specified
in the final rule. On January 21, 2005,
we published in the Federal Register a
notice (70 FR 3183–3184, Docket No.
03–080–5) announcing the availability
of a corrected version of the EA for
public review and comment. On April 8,
2005, we published in the Federal
Register a finding (70 FR 18252–18262,
Docket No. 03–080–7) that the
provisions of the final rule would not
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have a significant impact on the quality
of the human environment.
On March 11, 2005, we published a
document in the Federal Register that
gave notice that the Secretary of
Agriculture was delaying until further
notice the implementation of certain
provisions of the final rule with regard
to certain commodities (70 FR 12112–
12113, Docket No. 03–080–6).
On November 28, 2005, we published
in the Federal Register an interim rule
(70 FR 71213–71218, Docket No. 03–
080–8) that amended certain provisions
established by the January 2005 final
rule. The interim rule broadened the list
of who is authorized to break seals on
conveyances and allows transloading
under supervision of products transiting
the United States.
On March 14, 2006, we published in
the Federal Register a technical
amendment (71 FR 12994–12998,
Docket No. 03–080–9) that clarified our
intent with regard to certain provisions
in the January 2005 final rule and
corrected several inconsistencies within
the rule.
On August 9, 2006, we published in
the Federal Register a proposed rule (71
FR 45439–45444, Docket No. APHIS–
2006–0026) that proposed to amend the
provisions established by the January
2005 final rule by removing several
restrictions regarding the identification
of animals and the processing of
ruminant materials from BSE minimalrisk regions, and by relieving BSE-based
restrictions on hide-derived gelatin from
BSE minimal-risk regions. We solicited
comments concerning our proposal for
60 days ending October 10, 2006. On
November 9, 2006, we published a
document in the Federal Register (71
FR 65758–65759, Docket No. APHIS–
2006–0026) reopening and extended the
comment period until November 24,
2006. We received a total of 10
comments by that date. We are
considering the issues raised by the
commenters and will address them in a
separate rulemaking document.
Scope of the January 2005 Final Rule
The regulations established by the
January 2005 final rule and subsequent
amendments have allowed the
importation from BSE minimal-risk
regions of live bovines that are under 30
months of age when imported and when
slaughtered and that have been subject
to a ruminant feed ban equivalent to
that in place in the United States.
We did not attempt, for that
rulemaking, to assess the BSE risk
associated with the importation of live
bovines 30 months of age or older from
a BSE minimal-risk region. Our March
8, 2004, document that reopened the
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comment period on the November 2003
proposed rule stated that APHIS was
evaluating the appropriate approach
with regard to the importation of live
animals 30 months of age or older from
BSE minimal-risk regions, and would
address that issue in a supplemental
rulemaking proposal in the Federal
Register. The provisions in our January
9, 2007, proposed rule regarding live
bovines were the result of that
evaluation.
The regulations established by the
January 2005 final rule also provided for
the importation of the following
commodities derived from bovines of
any age: (1) Meat, meat food products,
and meat byproducts; (2) whole or half
carcasses; (3) offal; (4) tallow composed
of less than 0.15 percent insoluble
impurities that are not otherwise
eligible for importation under
§ 95.4(a)(1)(i) of the regulations; and (5)
gelatin derived from bones of bovines
that is not otherwise eligible for
importation under § 94.18(c) of the
regulations.
The January 2005 final rule and
subsequent amendments did not change
the regulations concerning the
importation of blood and blood
products from regions listed in
§ 94.18(a); the requirements for the
importation of blood and blood
products from BSE minimal-risk regions
remain the same as the requirements for
importation of blood and blood
products from other regions listed in
§ 94.18(a)—only serum and serum
albumin have been eligible for
importation. The January 2005 final rule
also did not change the regulations
concerning the importation of bovine
casings (defined as intestines, stomachs,
esophagi, and urinary bladders) from
regions listed in § 94.18(a); the
requirements for the importation of
bovine casings from BSE minimal-risk
regions remain the same as the
requirements for importation of bovine
casings from other regions listed in
§ 94.18(a)—only bovine stomachs are
eligible for importation.
The January 2005 final rule and
subsequent amendments allowed trade
to resume in many, but not all, of the
commodities that had been prohibited
importation from Canada following
detection of a BSE-infected cow in
Canada in May 2003. Following our
January 2005 final rule, we continued to
consider the BSE risk associated with
older bovines and other bovine products
from BSE minimal-risk regions—and
Canada in particular—including bovine
blood and blood products, bovine small
intestine other than the distal ileum,
and bovine casings, and included
provisions in our January 2007
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proposed rule for the importation of
those commodities.1
Peer Review of APHIS’ Risk
Assessment
As part of this rulemaking, APHIS
conducted an assessment that evaluated
the animal health risk to the United
States of BSE—i.e., the likelihood of
establishment and the potential impacts
of cases that may occur even without
establishment—as a result of importing
the bovine commodities considered in
this rule (APHIS 2006b). Our assessment
concluded that, over the 20 years of the
analysis, the BSE risk to the United
States is negligible. We made the risk
assessment available for public review
and comment at the time the proposed
rule was published.
In addition to making the risk
assessment available for review and
comment by the general public, we
requested an external, formal,
independent peer review of the
assessment by recognized experts in the
field, consistent with guidelines of the
U.S. Office of Management and Budget
(OMB 2004). The objective of the peer
review was to determine whether the
risk assessment was scientifically
sound, transparent, and consistent with
international standards (e.g., those by
the OIE); the application of external
assessments or models was appropriate;
and the assumptions were justified,
supported and reasonable. Comments
submitted by the public on the proposed
rule were submitted to the peer
reviewers for their consideration. The
peer review process was coordinated by
an independent private contractor.
The full peer review report may be
viewed at https://www.aphis.usda.gov/
peer_review/peer_review_agenda.shtml.
Additionally, we have included below,
under the heading ‘‘Final Report from
Peer Review of APHIS’ Risk Assessment
and Responses to Peer Reviewer
Questions and Recommendations,’’
APHIS’ responses to reviewer comments
that we consider representative of the
content-related questions and
recommendations of the report, and our
response to those questions and
recommendations. In summary, the
1 The regulations regarding BSE minimal-risk
regions apply to bison as well as cattle. In
§§ 93.400, 94.0, and 95.1 of the regulations, bovine
is defined as Bos taurus, Bos indicus, and Bison
bison. Although the research and other data cited
in this rulemaking refer to bovines other than bison
(i.e., to ‘‘cattle’’), there is no evidence to indicate
that the BSE susceptibility of bison differs from that
of cattle. We therefore assume that our conclusions
based on cattle-specific evidence discussed in this
rulemaking are also applicable to bison. Given that
no cases of BSE have been detected in bison, this
is likely a conservative assumption. The provisions
of this rule apply to bovines as defined in the
regulations, which include bison.
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reviewers found that the methods used
in the risk assessment were
scientifically rigorous in terms of using
existing literature and models
appropriately and making sound
assumptions and that the risk
assessment itself adhered to
international risk assessment standards.
The reviewers also agreed with the
conclusion that the likelihood of
establishment of BSE in the U.S. cattle
population is negligible.
In addition to being supportive of the
methods, evidence, and conclusions
presented by APHIS in the risk
assessment, the reviewers made several
useful suggestions for its improvement.
We made several clarifications and
updates in consideration of these
comments. While we expect that the
changes improve the transparency and
accuracy of the document, they do not
alter our conclusion that the risk to the
United States of BSE—i.e., the
likelihood of establishment and the
potential impacts of cases that may
occur even without establishment—
resulting from the changes outlined in
the proposed rule is negligible.
Removal of Partial Delay of
Applicability of Provisions of January
2005 Final Rule
Our January 2005 final rule made
eligible for importation from Canada
meat that is derived from bovines
slaughtered in BSE minimal-risk
regions, as well as certain other
specified commodities derived from
such bovines, provided certain specified
risk-mitigating conditions have been
met. The risk analysis we conducted for
that rulemaking indicated a low BSE
risk from such commodities derived
from bovines of any age if certain
conditions are met (APHIS 2004). These
conditions include the removal of those
tissues considered at particular risk of
containing the BSE agent in infected
animals (specified risk materials, or
SRMs). In that rulemaking, we
discussed regulatory requirements
implemented by FSIS in 2004 that
banned SRMs from the human food
supply in the United States, and we
stated that the Canadian Government
had established similar safeguards in
Canada.
Consequently, we provided that meat,
meat byproducts, meat food products,
and offal derived from bovines are
eligible for importation from BSE
minimal-risk regions if the following
conditions, as well as all other
applicable requirements of the
regulations, are met:
• The commodity is derived from
bovines that have been subject to a
ruminant feed ban equivalent to the
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requirements established by the U.S.
Food and Drug Administration at 21
CFR 589.2000;
• The commodity is derived from
bovines for which an air-injected
stunning process was not used at
slaughter; and
• The SRMs and small intestine of the
bovines from which the commodity was
derived were removed at slaughter.
Additionally we provided that tallow
composed of less than 0.15 percent
insoluble impurities that is not
otherwise eligible for importation under
9 CFR 95.4(a)(1)(i), and gelatin derived
from bones of bovines that is not
otherwise eligible for importation under
9 CFR 94.18(c) are eligible for
importation from BSE minimal-risk
regions, provided certain specified
conditions are met.
In the economic analysis we
conducted for the January 2005 final
rule, we evaluated the potential
economic effects of implementing that
rulemaking, including implementation
of the provisions allowing the
importation of meat and other
commodities derived from bovines
slaughtered in BSE minimal-risk regions
(APHIS 2004a).
In March 2005, APHIS published a
document in the Federal Register that,
pursuant to an announcement by the
Secretary of Agriculture on February 9,
2005, delayed the applicability of the
provisions in our January 2005 final rule
as they apply to the importation from
Canada of the following commodities
when derived from bovines 30 months
of age or older when slaughtered: (1)
Meat, meat food products, and meat
byproducts other than liver; (2) whole or
half carcasses; (3) offal; (4) tallow
composed of less than 0.15 percent
insoluble impurities that is not
otherwise eligible for importation under
9 CFR 95.4(a)(1)(i); and (5) gelatin
derived from bones of bovines that is
not otherwise eligible for importation
under 9 CFR 94.18(c).
In his February 9, 2005,
announcement, the Secretary stated that
because ongoing investigations into
recent finds of BSE in Canada in
animals over 30 months of age were not
complete, he felt it prudent to delay the
effective date for allowing imports of
meat from bovines 30 months of age and
over. He also indicated that the delay of
applicability would address concerns
that the January 2005 final rule allowed
the importation of beef from bovines 30
months of age or older, while
continuing to prohibit the importation
of live cattle 30 months of age or older
for processing in the United States. The
Secretary stated that the Department
would consider and develop a plan—
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based on the latest scientific
information and with the protection of
public and animal health as the highest
priority—to allow imports of live
bovines 30 months of age or older as
well as beef from animals 30 months of
age and older.
Since the date of the partial delay of
applicability of our January 2005 final
rule, we have obtained additional
information regarding all aspects of the
issues that prompted the delay of
applicability and have conducted
additional analyses in line with the plan
as described. The risk assessment for
this final rule demonstrates the
negligible BSE risk from the importation
of additional classes of live cattle,
including those 30 months of age or
older. This includes acknowledging the
potential risk pathway that could be
available if the SRMs from infected
imported cattle entered the ruminant
feed supply in contravention of current
feed regulations. The negligible risk
from the importation of live older cattle
therefore gives further support to the
conclusion of the risk analysis
conducted for our January 2005 final
rule regarding meat and meat products
derived from bovines of any age in BSE
minimal-risk regions. Specifically, the
risk is even lower for the importation of
meat and meat products, as the SRMs
will be removed in accordance with the
regulations, than for live bovines.
Therefore, this document will remove
the partial delay of applicability of the
January 2005 final rule. The removal of
the partial delay of applicability will
become effective on the date that the
other provisions of this document
become applicable. Including the
removal of the partial delay of
applicability in this final rule and
making it effective along with the other
provisions of this rule will enable
APHIS to more efficiently communicate
the necessary implementation
instructions to U.S. Customs and Border
Protection and to APHIS field
personnel. Additionally, it will provide
commercial entities more flexibility in
carrying out import planning based on
the relative economic merits of
importing live bovines or meat and
other products derived from bovines.
Because, for reasons of efficiency for
APHIS and the regulated community,
the Secretary has decided to remove the
delay in applicability as part of this
document, we looked at the economic
effects of doing so in combination with
allowing the importation of bovines
born on or after March 1, 1999.
Although we previously analyzed the
economic effects of allowing the
importation of meat and other products
derived from bovines 30 months of age
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or older, the economic analysis for this
rule provides an updated analysis.
Public Comments on the January 2007
Proposed Rule
We solicited comments concerning
our January 2007 proposal for 60 days
ending March 12, 2007. We received
close to 400 comments by that date. The
commenters included cattle industry
and farm bureau associations, consumer
groups, representatives of the Canadian
Government and other foreign countries,
State Departments of Agriculture, food
processing companies, individual cattle
producers, and other members of the
public.
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Subjects of Comments Received
A number of commenters supported
the rule and recommended no changes
to the proposed provisions. Other
commenters supported the rule in
general but recommended certain
changes or actions. Other comments
consisted only of recommended
changes, objections to the rule in
general or to specific provisions, or
requests for clarification. We discuss
below by topic the issues raised by
commenters and our response to those
comments.
General Opposition to Imports
Issue: A number of commenters
expressed general opposition to the
importation of any bovines or bovine
products from BSE minimal-risk
regions.
Response: It appears to us that these
commenters are not addressing just our
January 2007 proposed rule, but, rather,
also the January 2005 final rule that
recognized the category of BSE minimalrisk regions and established conditions
for the importation of certain ruminants
and ruminant products from such
regions.
As we discussed in the January 2005
final rule, the comprehensive analysis
and evaluation we conducted for that
rulemaking led to the conclusion that
the conditions specified in that rule for
the importation of ruminants and
ruminant products from BSE minimalrisk regions would be effective and
would therefore protect against the
introduction of BSE into the United
States. Our January 2007 proposed rule
considered expansion of the types of
commodities allowed importation from
BSE minimal-risk regions, based on an
evaluation of the risk (i.e., the
likelihood of establishment and the
potential impacts of cases that may
occur even without establishment) of
importing from Canada live animals,
blood and blood products, and the small
intestine excluding distal ileum.) Given
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the determination of negligible BSE risk
associated with the provisions of this
final rule, and the findings associated
with our 2005 final rule, there is no
scientific basis for increasing
restrictions from those already in effect
or being established in this rule.
Issue: A number of commenters
expressed opposition, without further
explanation, to the importation from
BSE minimal-risk regions of live
bovines 30 months of age or older and
to the importation of products derived
from such bovines.
Response: We discussed in our
January 2007 proposed rule the
rationale for our proposal to allow the
importation, under certain conditions,
of live bovines 30 months or older from
BSE minimal-risk regions. We discussed
further the assessment of the disease
risk of allowing such imports that we
conducted before issuing our proposal.
It is not clear to us which factors in our
risk assessment or discussion of
rationale were being addressed by those
commenters who expressed general
opposition to the importation of live
bovines 30 months of age or older. We
continue to consider the BSE risk from
importing live bovines under the
conditions specified in this rule to be
negligible.
Issue: Several commenters who
expressed opposition to the proposed
rule expressed concern that the agent
that causes BSE has yet to be fully
characterized. The commenters stated
that what we know about BSE is mostly
supposition, which should be a
compelling reason not to allow the
importation of cattle from a region of
known BSE outbreaks. One commenter
stated that research recently conducted
at Yale University suggests that one of
the agents that activates BSE may be
viral, which, according to the
commenter, implies that a feed ban is
effective only when the virus is not
present or active.
Response: As one of the commenters
noted, some researchers (Manuelidis et
al., 2007) suggest that diseases
characterized as transmissible
spongiform encephalopathies (TSEs),
such as BSE, may be caused by viruses,
although, at this point, no infectionspecific nucleic acids have been
identified.
Experimental data and
epidemiological studies strongly suggest
that contaminated feed containing
ruminant proteins derived from infected
animals was the source of the epidemic,
and that the epidemic was perpetuated
through the use of these materials in
ruminant feed. APHIS considers that
regardless of the characteristics of the
BSE causal agent, it is clear that the
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53317
epidemic was sustained and amplified
by the recycling of BSE infected cattle
into cattle feed. Despite the difficulty in
definitively determining the causal
agent of BSE, risk factors for
transmission of the agent have been
identified. The identification and
characterization of these risk factors
through epidemiological and
experimental study have allowed the
development of effective mitigations to
prevent BSE spread. The development
and demonstrated effectiveness of those
mitigations does not require
identification of the agent itself. We
consider mitigation measures that
address the risk factors for BSE to be
effective regardless of the precise nature
of the BSE agent.
Prevalence of BSE in Canada
Although the provisions of this rule
apply to any region recognized by
APHIS as a BSE minimal-risk region, at
present APHIS recognizes only one
country, Canada, as such a region.
Therefore, in evaluating the BSE risk of
implementing this rule, we conducted
an assessment of the risk of importing
bovines and bovine products from
Canada under the provisions of our
proposed rule (APHIS 2006b). In our
risk assessment, we laid out the likely
risk pathway (i.e., a series of
occurrences or steps necessary for
disease to enter and become
established).
In conducting our risk assessment,
one of the factors we took into account
was the prevalence of BSE in Canada,
since prevalence is one factor that
affects the likelihood of a BSE-infected
bovine being imported into the United
States. We received a number of
comments from the public that
addressed our estimate of the
prevalence of BSE in Canada. Although
some of the comments supported our
estimate of BSE prevalence in Canada,
in general the commenters maintained
that such prevalence is either higher
than we estimated, may be increasing,
or is uncertain, or that our methods of
estimating it were flawed. The
methodology we used to arrive at such
estimates is discussed in detail in our
risk assessment. However, to provide
some context for the issues raised by
commenters and discussed below, we
summarize here the models that we
used in conducting our assessment.
The number of BSE cases detected
through surveillance understates the
disease prevalence because exposed
animals may be incubating disease and
carrying infectious material in their
tissues without presenting clinical
symptoms. Like many transmissible
spongiform encephalopathies (TSEs),
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BSE has an incubation period of several
years. Therefore, the disease is not
detectable in its early stages with
current technology. Moreover,
surveillance will miss a proportion of
detectable cases. Therefore, we applied
statistical methods to the available
epidemiologic and surveillance data to
estimate, with attendant uncertainty, the
prevalence of BSE in Canada.
We used two related, but distinct,
methods to estimate BSE prevalence in
Canada: the BSurvE model and the
Bayesian Birth Cohort (BBC) model.
Given its international prominence, we
used the European Union (EU) BSurvE
model (Wilesmith et al., 2004, 2005),
recently developed for the purpose of
estimating BSE prevalence in national
herds. The BSurvE model is noteworthy
for its sound epidemiologic structure,
including stratifying cattle by age and
cause of death (i.e., healthy slaughter,
fallen stock, casualty slaughter, or
clinical suspect) and accounting for the
relative likelihood of detecting BSE in
various strata (EFSA 2004). The BSurvE
model structure calculates BSE
surveillance point values (random
sample size equivalents) represented by
targeted Canadian sampling of certain
groups of cattle in which BSE cases are
more likely to be detected. This
approach allows for the inclusion of
infected, but undetected, cases (such as
young animals in the early stages of
incubation) in the estimate, which
would be ignored by conventional
methods.
The other prevalence estimation
model that we used is the BBC model.
This model uses the BSurvE model
structure and incorporates additional
information. Unlike BSurvE, the BBC
model adopts a Bayesian statistical
framework to incorporate prior
information about the decreased
incidence of BSE observed in animals
born after a feed ban equivalent to the
initial ruminant-to-ruminant feed ban
introduced in the United Kingdom in
1988.
Issue: One commenter stated that BSE
has become ‘‘firmly established’’ in
Canada.
Response: We disagree with the
comment, which we consider to
erroneously equate disease presence,
which may be transient, with disease
establishment. In epidemiology, an
infectious disease has become
established in a population when the
disease is perpetuated in the population
without the need for reintroduction
from an external source. For example,
OIE’s sister agency, the international
Commission on Phytosanitary Measures
(CPM) defines plant pest establishment
as ‘‘the perpetuation, for the foreseeable
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future, of a nonindigenous biological
agent within an area after entry’’ (CPM
2001). With the implementation and
continuation of a feed ban in Canada, all
evidence points toward eventual
eradication, rather than perpetuation of
BSE in that country.
Issue: One commenter stated that,
since the time APHIS published its
January 2005 final rule classifying
Canada as a BSE minimal-risk region,
the Agency has presented no new
evidence that would support allowing
the importation from Canada of the
additional commodities discussed in the
proposed rule. In fact, stated the
commenter, evidence points to Canada
having a higher prevalence of BSE than
APHIS had previously determined.
Response: As discussed in our
January 2007 proposed rule, we
revisited our earlier conclusions and
policies by conducting a rigorous risk
assessment based on current available
scientific knowledge of the disease. We
used peer reviewed risk assessment
models in our analysis to estimate the
prevalence of the disease in Canada and
to analyze the likelihood of BSE
establishment in the United States and
the potential impacts of cases that may
occur even without establishment as a
result of the importation into the United
States of the bovine commodities
considered in this rule. The risk
assessment itself was peer reviewed by
experts in the field. As noted above, the
reviewers agreed with the conclusion
that the risk of establishment of BSE in
the U.S. cattle population is negligible
and noted that several assumptions in
the risk assessment actually overestimate the risk, so the overall finding
that the BSE risk is negligible is
reasonable. Based on the results of the
risk assessment, we concluded that we
could safely import Canadian cattle
born on or after March 1, 1999, blood
and blood products, and small
intestines, excluding the distal ileum.
Issue: Several commenters raised
questions about the ability to
statistically determine BSE prevalence
‘‘trends’’ in Canada, but reached
different conclusions. Some
commenters stated that the trajectory of
BSE prevalence in Canada cannot be
determined by available surveillance
data and that, therefore, BSE prevalence
in Canada may be increasing. On the
other hand, another commenter
requested that APHIS make clear that,
despite the Agency’s use of the BSurvE
Prevalence B estimate, prevalence
should not be assumed constant over
time. The commenter requested that
APHIS emphasize that lack of statistical
evidence that prevalence varies from
cohort to cohort is likely the result of
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inadequate statistical power,2 and that,
nevertheless, BSE prevalence in Canada
is most likely decreasing.
Response: In our risk assessment for
this rule, we acknowledge that, given
the rarity of BSE cases in Canada, the
surveillance data are unlikely to provide
adequate statistical power to detect any
trend. However, as discussed in the risk
assessment, we consider it likely that
the prevalence of BSE in Canada will
decrease over time. With so few total
BSE cases observed in Canada, the
statistical power to detect differences in
prevalence between cohorts is low. The
peer reviewers of our risk assessment
concur with our conclusion. (RTI 2007,
pp. 6–26, 6–27).
Issue: One commenter estimated the
Canadian BSE prevalence to be 6.4 cases
per million cattle. Further, the
commenter stated that this prevalence
estimate is smaller than the risk
estimate provided by one of APHIS’
own risk assessments for a more
pessimistic value of the misfeeding rate.
The commenter suggested that this
discrepancy reflects optimistic
modeling assumptions in APHIS’ risk
assessment.
Response: We disagree with the
commenter’s analysis. Although the
commenter’s alternative prevalence
estimate, based on a simple
extrapolation method, falls within the
90 percent confidence interval 3 of
APHIS’ BSurvE Prevalence B estimate
(2.4 to 6.8 cases per million adult cattle)
with an expected value of 3.9 per
million case per million adult cattle
(APHIS 2006c, table 5), it is based on
different assumptions. Based on an
analysis of BSE testing in the EU in
2001 and 2002, the commenter’s
prevalence estimate assumes that
targeted ‘‘risk cattle’’ are only 10 times
more likely to test positive for BSE than
non-targeted routinely slaughtered
cattle. Considering the BSE testing
conducted in the EU during 2001–2004
(EC 2005a, table 3, p. 23), cattle in the
2 The power of a statistical test is the probability
of rejecting the null hypothesis when it is false. The
power depends on the test level of significance, the
magnitude of effect under the alternative
hypothesis, sample size, and variability in the
population. Rice (1988, pp.361–364) describes the
calculation of statistical power for comparing two
independent samples.
3 A confidence interval is a statistical range with
a specified probability that a given parameter lies
within the range. For example, the 90 percent
confidence interval of a distribution indicates the
range of values that we are 90 percent certain
include the parameter value of interest. It extends
from the 5th percentile, or 5 percent confidence
level, at the low end of the distribution of the 95th
percentile, or 95 percent confidence level at the
high end of the distribution. Similarly, a 95 percent
confidence interval would extend from the2.5
percent confidence level to the 97.5 percent
confidence level.
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European BSE risk animals category
(emergency slaughter, clinical suspects,
and fallen stock) are 22 times more
likely to test BSE positive than cattle in
the healthy slaughter category. Using
the commenter’s simple extrapolation
method and these more up-to-date data
on BSE test positive ratio, the resulting
BSE prevalence estimate would be 2.9
per million cattle. Although actually
lower than the expected value for the
BSurvE estimate, this value also falls
within the 90 percent confidence
interval of the Agency’s BSurvE
Prevalence B estimate, described above.
APHIS calculated both the BSurvE
Prevalence B estimate and the Bayesian
Birth Cohort (BBC) prevalence estimate,
but judged the latter to better
characterize the BSE prevalence in
Canada over the next 20 years, due to
the expected downward pressure
exerted on the disease by a feed ban.
With regard to the commenter’s
suggestion of a discrepancy, the
commenter provides no specific
reference to ‘‘the risk estimate provided
by one of APHIS’ own risk
assessments,’’ but appears to refer to the
main body of the 2005 report of Cohen
and Gray (available at https://
www.fsis.usda.gov/PDF/
BSE_Risk_Assess_Report_2005.pdf),
which was prepared for the USDA’s
Food Safety and Inspection Service
(FSIS). Cohen and Gray (2005) do not
estimate Canadian BSE prevalence, but
rather the effect of introducing 500 BSEinfected cattle into the United States,
and the pessimistic misfeeding
assumption estimates that introduction
would result in an expected 2,600 new
cases over 20 years. There is no
discrepancy because this aspect of the
Cohen and Gray 2005 report is not
relevant to our estimate of Canadian
BSE prevalence.
Issue: Based on APHIS’’ statements
that animals are infected within their
first year, and that feed produced prior
to the feed ban would not be available
for longer than a year, one commenter
stated that additional undetected
infected animals must have existed and
been rendered in order to provide
infectivity to detected cases. Therefore,
stated the commenter, adding in these
‘‘undetected’’ animals raises the number
of Canada’s known and measurable BSE
cases rises from 10 to 14, and APHIS’
estimate of BSE prevalence in Canada
based on 10 animals is low.
Response: We disagree with the
commenter’s analysis and conclusion,
which assumes that we did not take into
account the possibility of undetected
cases of BSE in arriving at our
prevalence estimate. APHIS’ estimate of
the prevalence of BSE in Canada was
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adjusted to account for cases that would
not be tested and for false negative test
results. Also, although the bulk of feed
will be consumed within a year after it
is produced, residual infectivity may
remain in the feed supply chain for an
extended period. For example,
examination of BSE cases in animals
born in the United Kingdom after the
1996 ‘‘reinforced feed ban’’ suggests that
these animals may have been infected
from the persistence of the BSE agent in
residual feed in storage bins (SEAC
2005).
Issue: One commenter suggested that
it is likely that Canada has numerous
cattle over 30 months of age that are
presently incubating the BSE disease,
rather than just a few (4.1) as suggested
by APHIS.
Response: The estimate of 4.1 BSEinfected animals in the standing
Canadian adult cattle population was
based on the expected BSE prevalence
in Canada under the BBC model. Using
the estimated prevalence under BSurvE
Prevalence B resulted in an estimate of
23.2 BSE-infected animals in the
standing Canadian adult cattle
population. Although, quantitatively,
our risk assessment did not assume a
decline in BSE prevalence over the next
20 years, we qualitatively consider such
a decline to be likely because of
continued compliance with the feed
ban. Therefore, in assessing the BSE risk
associated with imports from Canada
over the next 20 years, we consider the
result of the BBC model to be the more
applicable prevalence estimate for use
in our quantitative exposure model.
Issue: One commenter indicated that
although it is unclear whether the
APHIS estimates of Canadian BSE
prevalence included the BSE case
confirmed on August 23, 2006, the
APHIS estimates certainly do not take
into account the case confirmed on
February 7, 2007.
Response: We estimated Canadian
BSE prevalence based on a 7-year
surveillance period through August 15,
2006. This surveillance period included
the detection of nine BSE cases of
Canadian origin reported through
August 2006. Through surveillance
conducted from August 16, 2006,
through April 2007, Canada detected
one BSE case born in 2000 and another
born in 2001 (CFIA 2007). The BSE
prevalence estimation methods used by
APHIS (2006a) require detailed data to
stratify tested cattle by age and cause of
death (healthy slaughter, fallen stock,
casualty slaughter, or clinical suspect)
that are unavailable for the more recent
surveillance period. However, we can
assess the sensitivity of our previous
Canadian BSE prevalence estimates by
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adding the two additional cases without
changing the BSE surveillance points
accumulated by Canada during the 7year surveillance period through August
15, 2006 (APHIS 2006a, table 4). 4 This
approach results in a revised table of
BSurvE points and BSE cases by birth
year cohort that reflects a total of 11 BSE
cases of Canadian origin reported
through April 2007 (APHIS 2007, table
i).
Using the same methods described in
USDA’s estimate of BSE prevalence in
Canada (APHIS 2006c), we obtain
updated Canadian BSE prevalence
estimates:
• BSurvE Prevalence B: 90 percent
confidence interval = 3.0–8.0 cases per
million adult cattle
• Bayesian Birth Cohort (BBC,
Winbugs): 90 percent confidence
interval = 0.47–1.2 cases per million
adult cattle
Because the updated confidence
intervals contain the previous expected
value estimates of 0.68 per million
(BBC) and 3.9 per million (BSurvE
Prevalence B) (APHIS 2006c), we
conclude that the prevalence estimate is
not sensitive to the addition of the two
additional BSE cases discovered in
Canada in August 2006 and February
2007.
Issue: One commenter stated that
APHIS’ expectation that the prevalence
of BSE in Canada will continue to
decline from its present minimal level
does not acknowledge that the
prevalence of BSE in Canada right now
is very uncertain. The commenter’s
independent estimate of the current
Canadian BSE prevalence is ‘‘on the
order of 4–6 per million.’’
Response: APHIS’ risk assessment
addresses the uncertainty in the
prevalence of BSE in Canada by
considering estimates that differ by
more than a factor of five (APHIS
2006b). The BBC prevalence estimate
has an expected value of 0.68 cases per
million adult cattle.5 The BSurvE
Prevalence B estimate has an expected
value of 3.9 per million. The
4 In the BsurveE model, specific ‘‘point values’’
are assigned to each test sample, based on the
surveillance stream or subpopulation of animals
from which it was collected, as well as the
likelihood of detecting infected cattle in that
subpopulation. A sample from the specific
surveillance subpopulation where BSE is most
likely to be detected—i.e., a middle adult clinical
suspect—provides the most surveillance points.
Conversely, a sample from the subpopulation where
BSE is least likely to be detected—generally routine
slaughter—provides the least points.
5 The BBC model provides a more precise
estimate of BSE prevalence in Canada by combining
the epidemiologic theory and application of
surveillance data underlying the BSurvE model
with additional information about the effect of the
feed ban on prevalence.
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commenter’s own method of
estimation—‘‘on the order of 4–6 per
million——provides an estimate on the
same order of magnitude as the BSurvE
Prevalence B estimate of current
prevalence. In either case, prevalence is
extremely low.
Issue: One commenter stated that,
although APHIS estimates that BSE
prevalence in Canada is about 6.8 or
more times greater than in the United
States (0.68 vs. 0.1 per million), this
does not adjust for the important fact
that the first BSE case in the United
States was imported from Canada.
Response: The APHIS October 2006
estimate of BSE prevalence in Canada is
based on the nine BSE cases of
Canadian origin that had been
confirmed in North America as of
August 23, 2006. This total includes a
case of BSE that was confirmed in
Washington State on December 25, 2003
(APHIS 2006c, p. 1). The estimate of
BSE prevalence in the United States
excludes this case.
Issue: One commenter stated that the
calculation of BSE prevalence in Canada
used in APHIS’ risk assessment
excluded the European-born case
detected in 1993.
Response: The 1993 Canadian BSE
case of European origin was likely part
of the original exogenous source of BSE
infectivity introduced into Canada that
caused the subsequent generation of
indigenous cases. Imported cases of BSE
reflect an exposure to the disease that
occurred elsewhere, and, therefore, are
not generally included in estimates of
prevalence that reflect native exposure.
Similarly, when APHIS estimated the
prevalence of BSE in the United States,
the BSE-infected cow of Canadian origin
that was detected in Washington State
in December 2003 was excluded from
the analysis, because it was an imported
animal. In addition, as noted in APHIS’
estimation of BSE prevalence in Canada
(APHIS 2006c, p. 5), in accordance with
OIE guidelines (which indicate that
surveillance points totals taken into
account in assessing a country’s BSE
risk be accumulated over a maximum of
7 consecutive years), the estimated
prevalence of BSE in Canada is based on
surveillance data accumulated over a 7year period beginning August 16, 1999.
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The 1993 case predates the OIE 7-year
period.
Issue: One commenter indicated that
APHIS should not take action on the
proposal until real surveillance data
(not model-based predictions) show that
the BSE problem has abated. The
commenter stated further that denying
Canada’s BSE problem, or assuming it
away with unvalidated and incorrect
risk modeling assumptions, does not
responsibly manage BSE risks to the
United States.
Response: We disagree with the
commenter. In low BSE prevalence
populations such as Canada,
surveillance at levels that meet or even
greatly exceed OIE guidelines provide
insufficient statistical power to reliably
detect changes in BSE prevalence over
time. In other words, starting with a
very low number of infected animals
makes it very difficult to statistically
demonstrate decreases in that number,
even when testing a relatively large
number of animals.
The OIE Guidelines for BSE
Surveillance (Type A) call for countries
to accumulate 300,000 BSE surveillance
points over 7 consecutive years in order
to detect with 95 percent confidence a
prevalence level of at least one case of
BSE per 100,000 animals (OIE 2006,
Appendix 3.8.4).
To illustrate the comparative
difficulty in demonstrating trends in
low versus high prevalence populations,
consider two hypothetical countries that
have accumulated 1 million BSE
surveillance points for each of two
cohorts: Animals born before and
animals born after the introduction of a
ruminant-to-ruminant feed ban. Under
this scenario, sampling levels in both
countries far exceed the OIE guidelines.
Assume, however, that the two
countries differ with respect to their
initial prevalence—i.e., the initial
prevalence in ‘‘Country A’’ is 1 infected
animal per 10,000 animals, while that in
‘‘Country B’’ is 1 infected animal per
100,000 animals.
For a given surveillance level, the
statistical power of a hypothesis test can
be evaluated as a function of the
supposed change in BSE prevalence
between cohort 1 (pre-feed ban) and
cohort 2 (post-feed ban). The
conventional minimum statistical power
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criterion is 80 percent. In other words,
the probability that a statistical analysis
will detect a true difference across
groups should be at least 80 percent.
The conventional significance level is 5
percent, meaning that we would
conclude that a result was nonrandom
if it were 5 percent or less likely to
occur by chance alone. In our
hypothetical scenario, the power of the
surveillance in the country with higher
prevalence, Country A, to detect a 50
percent decline in BSE prevalence is 98
percent. In comparison, the power of the
surveillance in the lower prevalence
Country B to detect a 50 percent decline
in BSE prevalence is only 25 percent. In
other words, if the Country B feed ban
actually led to a 50 percent decline in
BSE prevalence and the equivalent of 2
million random samples were collected
(6.7 times the level under the OIE
guidelines), there would still be a 75
percent chance of concluding that the
prevalence was unchanged from its
initial level of 1 infected animal per
100,000 animals.
An important implication of the low
statistical power of sampling in low
prevalence populations is that BSE
surveillance data are unlikely to provide
a purely statistical basis for making a
determination about the date when a
specific intervention (e.g., a ruminantto-ruminant feed ban) becomes effective,
even when large amounts of
surveillance data are available. For
example, according to the OIE (2007a),
the annual incidence of reported BSE
cases in the Netherlands dropped from
13.2 to 0.8 per million adult cattle from
2001–2005.6 Despite the EU BSE
surveillance requirements for testing all
risk animals over 24 months of age and
all healthy slaughter cattle over 30
months of age, Figure 1 shows that
application of the BSurvE (Prevalence
A) model to Netherlands BSE
surveillance data does not yield
sufficient statistical power to draw clear
distinctions among birth year cohorts as
prevalence declines (Figure 1).
6 The OIE Terrestrial Animal Code (Chapter
1.1.1., Article 1.1.1.1) defines incidence as ‘‘the
number of new cases or outbreaks of a disease that
occur in a population at risk in a particular
geographical area within a defined time interval
(OIE 2006b).’’
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Note that, in figure 1, there is a
decrease in estimated prevalence
between 1998 birth-year cohorts and
1999 birth-year cohorts, while, at the
same time, there is an increase in the
upper confidence limit. This apparent
paradox is indicative of another
shortcoming of relying on surveillance
data alone to determine whether BSE
prevalence has been reduced. Because
fewer animals from the most recent
birth year cohorts are tested when sent
to slaughter, uncertainty about the
prevalence in the most recent cohorts is
much greater than in older cohorts.
Furthermore, the lower likelihood of
detecting BSE in young infected animals
means that the young animals that are
tested contribute relatively little to
reducing uncertainty in the true (as
opposed to apparent) BSE prevalence.
These two sources of uncertainty in
young birth cohorts (low numbers of
animals tested, and little value in the
surveillance data that are gathered from
them) cause an asymmetrical increase in
the upper limit of the confidence
interval compared to the lower
confidence limit. This effect on the
upper confidence limit on BSE
prevalence is most pronounced for the
most recent birth year cohorts which are
less likely to be tested and will not have
lived long enough to manifest BSE, even
if they have been infected. Wilesmith et
al. (2004, figure 3) further illustrates this
same concept.
Consequently, if the effectiveness of a
country’s safeguards against BSE
amplification were determined strictly
by setting a tolerance for the upper
confidence limit on BSE prevalence
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associated with the ‘‘real surveillance
data,’’ one might reach the incorrect
conclusion that prevalence is
increasing, when in actuality, the result
is simply due to testing fewer and
younger animals in the most recent birth
year cohorts. Finally, relying solely on
surveillance data fails to account for
under reporting of disease due to the
lack of diagnostic sensitivity to detect
BSE at an early stage of disease. By
accounting for the possibility of false
negative test results, epidemiologic
models such as BSurvE are recognized
as providing a more accurate estimate of
true BSE prevalence than the apparent
prevalence measured by surveillance
data alone.
Issue: One commenter stated that the
output from the BSurvE model used by
Canada in 2005 grossly underestimated
Canada’s 2006 and 2007 BSE prevalence
and, therefore, the BSurvE model is
unreliable for estimating Canada’s BSE
prevalence. The commenter stated
further that, at the minimum, APHIS
should determine the erroneous inputs
that resulted in the failed prediction in
2005 and correct them.
Response: In the risk assessment
conducted for this rulemaking, APHIS
used its own prevalence estimate, not
that of the Canadian Food Inspection
Agency’s (CFIA’s) 2006 prevalence
estimate, which was not based on
BSurvE, but on a modified version that
appears similar to the APHIS BBC
model. The commenter cites CFIA’s
Assessment of the North American BSE
Cases Diagnosed from 2003–2005 (Part
II), which states that ‘‘when the BSurvE
model was recently applied to Canada’s
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statistics and adjusted to account for the
effectiveness of the 1997 feed ban (based
on experiences with the 1988 feed ban
in the United Kingdom), the resulting
prediction was that it could be expected
that three infected animals remain
within the national herd’’ (CFIA 2006,
p. 13).
APHIS’ estimation of BSE prevalence
in Canada (APHIS 2006c) is that the
expected prevalence values under the
BBC and BSurvE Prevalence B models
correspond to an expected number of
BSE-infected animals in the standing
Canadian adult cattle population of 4.1
and 23.2, respectively. APHIS further
explains that it is important to note that
this range of prevalence estimates
represents uncertainty and not
variability. BSE-infected animals are
recruited into and exit from the adult
cattle population over time, but at a
given point in time, the number of
infected animals in the population is a
fixed but uncertain value.
Assuming the overall probability of
infection remains constant over time,
the actual number of infected cattle in
the population at any given point in
time would still vary randomly about
the mean. This variability is
incorporated in the model supporting
the exposure assessment for live bovines
by means of the Poisson variability
distribution. Assuming a fixed mean
prevalence of 4.1 and 23.2 BSE infected
animals in the standing adult cattle
population in Canada, the 95th
percentile of the Poisson distribution
are 7 and 31 BSE-infected animals in
any given year, respectively. We note
that these numbers are greater than the
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five BSE cases detected in Canada in
2006, which means that the greatest
number of Canadian BSE cases
identified in a single surveillance year
is lower than even the 95th percentile
of distribution.
Issue: One commenter stated that, if
the United States were finding BSE
cases at the same rate as in Canada, this
would translate into roughly 40 BSE
cases detected in the United States since
January 2006, which would be regarded
as a large number. The commenter
stated further that, at this time, the BSE
situation in Canada does not appear to
be improving.
Response: We do not agree with the
commenter. The commenter’s
conclusion appears to be based on a
cursory estimate and does not provide
an accurate comparison of BSE cases
detected in Canada with a comparable
number that would have been detected
in the United States, given the larger
U.S. cattle population. The commenter’s
comparison fails to take into account
other years of surveillance, as well as
the age and surveillance stream of tested
animals. These data are extremely
important for estimating BSE
prevalence. A comparison based solely
on the number of detected cases ignores
infected animals with unapparent or
undetected infections.
Table 1 provides a direct comparison
of the estimated BSE prevalence in the
current standing adult cattle population
of the United States and Canada,
respectively, using identical estimation
methods (APHIS 2006a; 2006c).
TABLE 1.—COMPARISON OF ESTIMATED BSE PREVALENCE IN THE
CURRENT STANDING ADULT CATTLE
POPULATION OF U.S. AND CANADA
BSE Prevalence Estimation
Method
Country
BSurvE
prevalence B
BBC
Expected value
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US ..................
Canada ..........
0.18 × 10¥6
3.9 × 10¥6 ...
0.10 × 10¥6
0.68 × 10¥6
Despite the higher estimated BSE
prevalence in the current standing adult
cattle population in Canada compared
to the prevalence of BSE in the standing
adult cattle population in the United
States, APHIS finds that, because of the
extremely low BSE prevalence in
Canada and the high levels of BSE
controls in both Canada and the United
States, the risk to the United States (i.e.,
the likelihood of establishment of BSE
in the United States and the potential
impacts of cases that may occur even
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without establishment) as a result of
importing from Canada the bovine
commodities considered in this rule is
negligible (APHIS 2006b). Furthermore,
as stated in our risk assessment, we
expect that the prevalence of BSE in
Canada will decrease continuously over
the next several years. Peer reviewers of
our risk assessment agreed (RTI 2007).
Issue: One commenter stated that
Canada’s ratio of positive cases per
10,000 cattle tested exceeds the ratio of
22 of the 25 EU-member countries; that
only the ratios for the United Kingdom,
Portugal, and Spain exceed Canada’s
2006 ratio. The commenter noted
further that even the countries of
Ireland, Germany, and France, each of
which are considered to have had
widespread BSE exposure, have a lower
ratio for positive cases detected per
10,000 head tested than does Canada.
Another commenter stated that Canada’s
BSE prevalence is higher than that for
Denmark, Belgium, and Austria, and is
comparable to the rate in Germany. This
commenter, who estimated the
Canadian BSE prevalence to be 6.4 cases
per million cattle, stated further that no
one considers countries with a reported
BSE rate of 1 to 2 cases per million
animals (e.g., Denmark, Belgium and
Austria) to have a minimal BSE risk,
and that Canada is not a BSE minimalrisk region in any ordinary sense.
Response: The commenters’
statements ignore important differences
in BSE surveillance and cattle
populations among countries, and a
comparison based simply on the
proportion of positive cases per number
of cattle tested is inconsistent with the
prevalence estimate approach taken by
one of the commenters, as well as the
prevalence estimate used by APHIS.
Although calculating the proportion of
infected animals detected per number of
tested animals can serve as a useful tool,
depending on the purpose for the
calculation, it is not an estimate of
prevalence. Rather, prevalence is
defined as the number of infected
animals in the total population at a
given point in time. On the other hand,
the calculation conducted by the
commenter who referred to the ratio of
positive cases per 10,000 cattle tested is
similar to that conducted by the U.S.
Department of Health and Human
Services, Centers for Disease Control
and Prevention (CDC). In May 2007,
using data similar to that analyzed by
APHIS for this rulemaking, CDC
calculated the proportion of Canadianborn BSE cases identified by Canadian
authorities in relation to the total
number of animals tested in that
country. CDC then made a like
calculation regarding BSE cases in U.S.-
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born cattle and compared the Canadian
and U.S. results (CDC 2007). Unlike the
estimate used by APHIS in the risk
assessment for this rule, the CDC
calculation is not an estimate of the
prevalence of BSE in Canada, nor of the
prevalence in the United States.
Although the type of calculations
conducted by CDC can be useful in
comparing relative proportions of BSE
detections per number of cattle tested,
they do not, as noted above, constitute
an estimate of prevalence.
The number of disease detections per
total number of animals tested can be
influenced by the criteria used for
choosing animals for testing. For
instance, Canada, like the United States,
conducts targeted BSE surveillance,
sampling those animals where disease is
most likely to be detected if present. In
contrast, EU countries routinely test
large numbers of healthy animals at
slaughter. Approximately 80 percent of
cattle tested for BSE in the EU during
2001–2004 were healthy slaughtered
animals, but ‘‘risk animals’’ were 22
times more likely to test positive (EC
2005a). One study (Giovannini et al.,
2005) estimates the true prevalence of
BSE infection in several EU countries.
Based on BSE testing in 2001, although
Denmark, Finland, and the Netherlands
had a lower proportion of positives per
test than Canada, the estimated
prevalences from this study for those
three countries were higher than the
expected values of our Canadian BSE
prevalence estimates using the BBC
estimation method (0.68 cases per
million adult cattle) or BSurveE
Prevalence B (3.9 cases per million
adult cattle). Giovannini et al. (2005)
estimated the following 90 percent
confidence intervals for the prevalence
of BSE infection: Denmark, 9 to 38 cases
per million animals; Finland, 29 to 110
cases per million animals; and
Netherlands, 8 to 34 cases per million
animals. The methods used by APHIS to
estimate Canada’s BSE prevalence,
including the BSurvE model developed
by the EU Transmissible Spongiform
Encephalopathies Community Reference
Laboratory, account for the cattle
population demographics, the age and
surveillance category of animals tested,
and the insensitivity of BSE diagnostics
with regard to detection of the disease
at an early stage of development.
The comments are based on an
inappropriate comparison of a statistical
estimate of the true BSE prevalence in
Canada to the crude rate. Table 2 below
compares the crude reported BSE rates
in all five countries in 2005. Comparing
the reported BSE rate of Canada to those
of the countries listed by the
commenters shows that Canada’s
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reported rate is at least an order of
magnitude below that of the others.
TABLE 2.—REPORTED BSE RATES IN
5 COUNTRIES
Country
Canada ...............................
Denmark .............................
Belgium ...............................
Austria .................................
Germany .............................
Reported BSE
cases per
million adult
cattle—2005
0.145
1.289
1.448
2.114
4.965
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Source: OIE (2007a).
The problem with comparing the
crude reported rate of BSE detection to
the estimated true BSE prevalence is
illustrated by the situation in Belgium.
The reported rate of BSE in Belgium
peaked in the 2001 surveillance year at
28.22 cases detected per million adult
cattle (OIE 2007a). In comparison,
Saegerman et al. (2004) applied the
BSurvE model to the Belgian BSE
surveillance data and estimated that the
actual BSE prevalence in Belgium
peaked at approximately 400 cases per
million adult cattle in the 1995 birth
year cohort. (The lag between the 1995
birth year and the 2001 surveillance
year is consistent with the long BSE
incubation period.)
With regard to the comment that
countries with 1 to 2 cases per million
animals are not considered to present
minimal risk, APHIS notes that, prior to
the 2005 revisions in the OIE guidelines
on BSE, countries with a reported BSE
rate of 1 to 2 cases per million animals
could satisfy the prevalence criterion for
the pre-2005 OIE BSE minimal-risk
classification. Under the 2004 OIE
Terrestrial Animal Health Code (Article
2.3.13.5), the criteria for a BSE minimalrisk country included a reported rate of
less than two cases per million during
each of the last four consecutive 12month periods within the cattle
population over 24 months of age. The
OIE Code was modified in 2005 to
include a revised country categorization
system which more accurately reflected
current scientific understanding of BSE.
These modifications streamlined the
number of country categories to three
(negligible, controlled, or undetermined
BSE risk) and also eliminated the
numeric prevalence criteria for
classifying the BSE risk status. The
previous OIE minimal-risk category is
now incorporated into the controlled
risk category. We note that in 2007, the
OIE recognized Switzerland as a BSE
controlled risk region. Switzerland had
a reported rate of 5.4 BSE cases per
million adult animals in 2006 (OIE
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2007a), greater than the 1 to 2 cases per
million animals cited by the
commenters.
APHIS disagrees with the
commenter’s statement that Canada
does not qualify as a BSE minimal-risk
region. APHIS regulations at § 94.0
define the standards for a region to be
designated as a minimal-risk region.
These include the standard that the
region maintain ‘‘risk mitigation
measures adequate to prevent
widespread exposure and/or
establishment of the disease.’’ Canada
continues to meet this standard. The
commenters provided no specific
evidence to document how or why
Canada does not meet the APHIS
standards.
Issue: One commenter stated that the
prior information [information using
data from the United Kingdom feed ban]
incorporated into the Bayesian models
used to estimate prevalence of BSEinfected cattle in Canada may have
resulted in estimates that are biased
downward (to a limited degree) from the
true burden. However, stated the
commenter, the Bayesian models used
to estimate prevalence in Canada (as of
August 2006) are basically sound and a
better approach than relying on the
BSurvE Prevalence B estimate. Further,
said the commenter, given the proviso
that the models could overestimate the
effectiveness of the feed ban, it is most
likely that the actual prevalence of
infected animals is between 0.68 and 3.9
animals per million adult cattle. The
commenter stated that because it is
likely that the Canadian feed ban was at
least as effective as the initial United
Kingdom feed ban, and based on
available data, the true BSE prevalence
in Canada is probably substantially
closer to 0.68 cases per million animals
than to 3.9 cases per million animals.
Conversely, several commenters
suggested that APHIS rejected the
higher prevalence estimate of the
BSurvE model for the lower prevalence
estimate of the BBC model, and that the
BBC model prevalence estimate is not
realistic in light of recent data.
Response: Although APHIS
considered the results of both the
BSurvE and the BBC prevalence
estimation models, we consider the
result of the BBC model as the more
likely prevalence estimate to apply to
the assessment of BSE risks associated
with imports from Canada over the next
20 years in our quantitative exposure
model, for the following reasons. APHIS
estimated Canadian BSE prevalence
based on surveillance conducted
through August 15, 2006. (Note: This
time period includes all cases of
Canadian origin reported through
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August 2006 (APHIS 2006c).) From
August 16, 2006, through April 2007,
Canada accumulated approximately
44,980 additional BSE samples and
detected two BSE cases (one confirmed
on February 7, 2007, and another
confirmed on May 2, 2007). Based on
the negative binomial likelihood ratio,
which considers the number of negative
tests prior to one or more positives, the
BSurvE Prevalence B estimate (with
expected value of 3.9 cases per million
animals) is indeed far more likely to be
true than is the BBC prevalence estimate
(with an expected value of 0.68 cases
per million animals) for the current
standing Canadian cattle population.
However, the primary purpose of
characterizing BSE prevalence in
Canada’s current standing herd (APHIS
2006c) was not to discuss or assume its
implications for the present, but rather,
to estimate prevalence for use as an
input for the Harvard exposure model
used in the Exposure Assessment of the
analysis. Because BSE has a long
amplification cycle (it takes an average
of 7 years from the time that one animal
is exposed, to the time that another
might be exposed from infectivity
produced by the first animal), the
Harvard model is typically run with 20year simulations to include roughly 3
amplification cycles. The prevalence
estimates contained in APHIS’
estimation of BSE prevalence in Canada
(APHIS 2006c) are applied, unchanged,
to the cattle imports projected over the
next 20 years (2007–2026). Since we
expect that the true prevalence will
drop from its current level (whatever
that may be), we anticipate that the
lower, BBC estimate is a more realistic
prediction (or even an overestimate) of
average prevalence levels over this time
frame. Consequently, APHIS considers
the result of the BBC model, which
incorporates the effect of a feed ban, to
be better for application to the
quantitative assessment of BSE risks
associated with imports from Canada
over this time period. In order to
determine the impact of this assumption
on the results, we applied the BSurvE
estimate to the exposure model. We note
that the likelihood of BSE establishment
remained negligible (R0 of 0.079, which
is far less than 1), as did the potential
impact of cases even without
establishment (less than 4 clinical cases)
over the 20 years of the analysis.
Issue: One commenter suggested that
the APHIS risk model is not trustworthy
because it has not been shown to have
predictive validity and does not explain
or predict a sustained flow of BSE cases
from one geographic area (the Alberta
region in Canada).
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Response: It is not clear to us from the
comment which model the commenter
is referring to. Consequently, in this
response, we discuss the Harvard model
and the prevalence models used by
APHIS. In either case, we disagree with
the commenter’s conclusion that the
APHIS risk model is not trustworthy.
The plausibility of the Harvard model
was established by comparing its
predictions for Switzerland against the
observed progression of BSE within that
country’s cattle herd (Cohen et al.,
2003). It is not clear from the comment
how the predictive validity of an
infectious disease model is to be
demonstrated over a 20-year time
horizon, or how the model has failed to
explain or predict the observed data.
Regarding a sustained flow of BSE cases
from one geographic area, assuming a
constant proportion of BSE infected
cattle in the herd, more BSE cases are
found where large cattle populations
exist.
As we discuss above in response to
another issue raised by commenters,
APHIS’ estimation of BSE prevalence in
Canada (APHIS 2006c) concludes that
the expected prevalence values under
the BBC and BSurvE Prevalence B
models correspond to an expected
number of BSE-infected animals in the
standing Canadian adult cattle
population of 4.1 and 23.2, respectively.
Further, the prevalence estimates
represent uncertainty and not
variability. At any given point in time,
the number of infected animals in the
population is a fixed (although
uncertain) value, although over time the
actual number of infected cattle in the
population would vary randomly about
the mean of the probability distribution,
as BSE-infected animals are recruited
into and exit from the adult cattle
population (i.e., some are newly
infected and some die). Even assuming
that the probability of infection remains
constant, over time the actual number of
infected cattle in the population would
vary. This variability is incorporated in
the model supporting our exposure
assessment for live bovines by means of
the Poisson variability distribution.
Assuming a fixed mean prevalence of
4.1 and 23.2 BSE-infected animals in the
standing adult cattle population in
Canada, the 95th percentile of the
Poisson distribution is respectively 7
and 31 BSE-infected animals in any
given year. As we noted above, these
numbers are greater than the five BSE
cases detected in Canada in 2006, which
means that the greatest number of
Canadian BSE cases identified in a
single surveillance year is lower than
even the 95th percentile of distribution.
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While this observation does not
statistically validate (confirm) the
APHIS estimates of Canadian BSE
prevalence, neither does it invalidate
them, as the commenter seems to
suggest. Furthermore, the prevalence
estimates are applied not only to the
current standing population, but also to
the next 20 years.
BSE Data From the United Kingdom
In our January 2007 proposed rule
and its supporting risk assessment, we
discussed data associated with a
ruminant-to-ruminant feed ban in the
United Kingdom and indicated that
experience in the United Kingdom
demonstrates that implementation of a
ruminant-to-ruminant feed ban causes
BSE prevalence to decrease. We noted
that animal feed restrictions were
implemented in the United Kingdom in
1988, when the use of ruminant MBM
in ruminant animal feed was banned. In
September 1990, the use of specified
bovine offals was banned for use in any
animal feed. This ban prohibited the use
in any animal feed of bovine tissues
with the highest potential concentration
of infectivity. In 1994, the use of
mammalian protein—not just ruminant
protein—was banned from ruminant
feed. In 1996, feeding of any farmed
livestock, including fish and horses,
with mammalian MBM was completely
banned. As a result of reducing the
recycling of infectivity, the annual
incidence of BSE fell by 99.4 percent,
from 36,680 in 1992 to 203 in 2005
(DEFRA 2006b). There is, therefore,
every reason to expect downward
pressure on the prevalence of BSE in
any country that implements a feed ban.
Issue: One commenter stated that, of
180,986 confirmed cases of BSE in Great
Britain, the year of birth of the infected
animal is unknown in 43,342 cases, and
the large percentage of animals whose
birth year is unknown casts doubt on
the ability to determine the timeframe of
an effective feed ban and, and further,
makes it doubtful that all BSE-infected
cattle in Canada are going to show
clinical signs of the disease only if they
were born before March 1, 1999. The
commenter also stated that Japan has
reported cattle as young as possibly 20
months of age or younger as testing
positive for BSE.
Response: It is not clear to us how the
information presented by the
commenter supports the conclusions the
commenter reached. However, we
consider it useful to provide some
clarification regarding the information
presented. With regard to the proportion
of BSE cases in Great Britain for which
the date of birth is unknown, our risk
assessment included a sensitivity
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analysis that takes into account that
general source of uncertainty.
(Sensitivity analysis evaluates the
degree to which changes in the
assumptions used in a model affect the
model’s results.) We made no
assumptions as to whether Great
Britain’s feed ban is or has been
effective, but applied the same
proportional drop in cases observed in
the United Kingdom to the Bayesian
analysis that was performed to estimate
BSE prevalence in Canada’s standing
cattle herd.
The commenter’s statement that it is
doubtful that only animals born before
March 1, 1999, would show clinical
signs of BSE indicates a potential
confusion between the likelihood of
exposure as expressed in terms of the
date of the effectively enforced feed ban
(and, thus, the potential for exposure)
and the likelihood of an exposed animal
developing clinical signs (which is
based on age and amount of exposure,
and the amount of time that has elapsed
since exposure). In neither our risk
assessment nor our proposed rule do we
conclude that only infected animals
born before March 1, 1999, would show
clinical signs of the disease. Based on
Canada’s system of regulations,
compliance and enforcement, and the
length of time we expect pre-feed ban
feed to persist in the system, we
conclude that animals born on or after
March 1, 1999, have an extremely low
likelihood of exposure to BSE. Any
animal, however, exposed to an
infectious dose of the BSE agent and
allowed to live to the end of its
incubation period, would likely exhibit
clinical signs.
Regarding the age of cattle diagnosed
with BSE in Japan, the comment did not
contain sufficient information for us to
determine and respond to the relevance
of the statement to the remainder of the
comment.
Issue: One commenter questioned the
effectiveness of APHIS’ use of United
Kingdom surveillance numerators to
estimate Canada’s BSE prevalence.
Specifically, the commenter stated that
‘‘Nowhere * * * is incidence reported.
Cases (without reference to a population
at risk) are used. This may be important
because the manner in which BSE cases
were counted changed over time in the
[United Kingdom].’’
Response: We acknowledge that
changes over time in BSE surveillance
and in the size and demographics of the
cattle population do contribute to the
uncertainty about the efficacy of the
initial, ruminant-to-ruminant feed ban
introduced in the United Kingdom in
1998. However, the United Kingdom’s
Department for Environment, Food, and
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the initial United Kingdom ruminant-toruminant feed ban is uncertain.
Nonetheless, the United Kingdom’s
experience and data are important and
useful to our risk assessment and
analyses. In addition, the Peer Review
Report (RTI 2007, p. ES–2) noted that
‘‘[all reviewers] agreed that the evidence
from the United Kingdom * * * and
Europe that the feed ban is effective is
reasonable to consider in the case of
Canada.’’
Issue: Several commenters noted the
differences in the feed bans in the
United Kingdom and Canada in stating
that it is not valid to draw conclusions
about the likely prevalence of BSE in
Canada by extrapolating from the rate of
decline in BSE cases in the United
Kingdom following implementation of a
feed ban there. The commenters noted
that (until expanded this July) the feed
ban in Canada prohibited the feeding of
ruminant material to ruminants. In
contrast, said one commenter,
significant declines in the number of
confirmed BSE cases in the United
Kingdom did not occur until the United
Kingdom took stronger measures,
ultimately banning the feeding of all
mammalian protein to food animals in
2001. The commenter suggested that the
United Kingdom’s experience in
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particular clearly shows that ruminantto-ruminant feed bans do not drastically
curtail the number of confirmed BSE
cases and that much stronger measures
are needed to eradicate the disease.
Response: The comments appear to
confuse the absolute level of BSE in the
United Kingdom with its rate of decline.
The comments also ignore the BSE
incubation period and the effects of
other concurrent measures, trends, and
events in the United Kingdom. The
number of BSE cases in United
Kingdom birth year cohorts (all cattle
born in a given year) has continued to
decline since peaking in 1987. With the
exception of the 1996 birth year cohort,
it is not readily apparent that there has
been any significant change in the rate
of decline in birth year cohort
prevalence after the United Kingdom
introduced the initial ruminant-toruminant feed ban in 1988 (figure 2). As
of March 1, 2007, the United Kingdom
had confirmed two BSE cases in animals
born after 2001, but due to the long BSE
incubation period, it is reasonable to
expect that ongoing surveillance may
detect additional cases in animals born
after 1998.
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Rural Affairs (DEFRA) does not report
BSE surveillance results by birth year
and surveillance class (e.g., active or
passive surveillance, animal health
status). Ideally, such data could be
entered into BSurvE or a similar model
to estimate true BSE prevalence for all
United Kingdom birth year cohorts
since the onset of the epidemic. This
process would permit not only an
improved estimate of the effect of the
initial feed ban but also of the
incremental impact of additional
measures that were subsequently
introduced. DEFRA has reported backcalculation model estimates of true BSE
prevalence in cohorts born after 1995 to
assess the effects of the ‘‘reinforced feed
ban’’ introduced by the United Kingdom
in August 1996 (DEFRA 2005, 2006b).
However, we are unaware of any
published estimates of true BSE
prevalence in the United Kingdom for
the 1987–1995 birth year cohorts based
on up-to-date surveillance results.
Issue: One commenter stated that
APHIS is wrong to assume that the
United Kingdom data regarding the
effectiveness of the feed ban can be
applied directly to the situation in
Canada.
Response: We acknowledge that the
applicability to Canada of the data from
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for all farm animals (the ‘‘reinforced
feed ban’’), a selective cull, and the
over-30-month rule limiting the age of
animals that could be slaughtered for
food. As shown in figure 3, the size of
the United Kingdom cattle population
began a marked decline in 1996,
punctuated by a drop associated with
the foot and mouth disease (FMD)
outbreak in 2001.
In addition to the declining cattle
population size, other confounding
variables, such as changes in cattle
population demographics and BSE
surveillance practices, make it difficult
to ascertain the independent or marginal
effect of any single measure on the
decline of BSE in United Kingdom birth
year cohorts. At this time, it appears
that the confluence of events and
measures of 1996 may have hastened
the waning of BSE in the United
Kingdom, but the decline was underway
in 1988.
Issue: One commenter indicated that
scientific studies in France and Britain
have found that, after a ruminant-toruminant feed ban was put into place,
the subsequent incidence of BSE was
correlated to pig density, and that the
new Canadian BSE feed rule, to be
implemented in July 2007, is, according
to the commenter, similar to, but weaker
than, the September 1990 United
Kingdom SBO [Specified Bovine Offals]
ban. The commenter stated that, by not
following the lead of the United
Kingdom [and banning the feeding of all
mammalian protein to food animals],
the proposed CFIA SRM ban may
reduce but will not eliminate the risk of
BSE in Canada.
Response: Two studies—Abrial et al.
(2005) and Stevenson et al. (2005)—
indicate a correlation between cases of
BSE born after a ruminant-to-ruminant
feed ban was implemented and areas of
higher pig density in France and Britain.
These studies indicate the potential for
cross-contamination of livestock feeds
after ruminant-derived protein was
excluded from ruminant feed.
Eventually, each country and the EU
adopted regulations prohibiting the
inclusion of any animal protein in
livestock feed. At this time, however, it
is not possible to ascertain the extent, if
any, to which establishment of a more
restrictive feed ban had any impact on
the rate of BSE decline in EU Member
States beyond the feed controls already
in effect.
As discussed previously, the number
of BSE cases in United Kingdom birth
year cohorts began to decline in 1988,
the year the initial ruminant-toruminant feed ban was introduced.
Although France initially introduced a
ban on mammalian MBM in cattle feed
in July 1990—not a ruminant-toruminant feed ban—the European
Commission Scientific Steering
Committee concluded that the French
feed ban adopted in 1990 ‘‘was likely
not effectively enforced until 1994/
1995.’’ (ECSSC 2000, p. 30). Based on
testing in 2001–2002, Bonnardiere et al.
(2004) found a significant increase in
French BSE prevalence between the July
1993–June 1994 and July 1994–June
1995 cohorts, followed by a significant
decrease in BSE prevalence in birth
cohorts born in France after June 1995.
More recently, active surveillance
during 2001–2005 also indicates that the
number of BSE cases per cohort peaked
in France in the 1995 birth year cohort
and declined thereafter (EC 2006, table
B20).
In Europe more generally, based on
active surveillance during 2001–2005,
the number of BSE cases per birth year
cohort in the original EU Member States
(EU 15), excluding the United Kingdom,
was on the decline after the 1995 birth
year cohort. In June 1994, the EU
banned the feeding of mammalian MBM
to ruminants. However, among EU
members, only Belgium, Germany,
Greece, Italy, Luxembourg, and Spain
had no feed ban in place prior to the
1994 EU-wide measure (Court of
Auditors 2001). In June 2005, the
European Commission issued the
‘‘Report on the Monitoring and Testing
of Ruminants for the Presence of
Transmissible Spongiform
Encephalopathy in the EU in 2004’’ and
observed that the impact of the 2001
‘‘total feed ban’’ (EU Regulation 999/
2001) cannot yet be assessed due to the
long BSE incubation period. As noted in
the discussion of the decline of BSE in
the United Kingdom, it is reasonable to
expect that ongoing surveillance may
detect additional cases in animals born
after 1998.
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Shortly after the emergence of vCJD
was publicly recognized in March 1996,
the United Kingdom introduced several
BSE-related measures, including the ban
on the use of mammalian MBM in feed
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potential impacts of cases that may
occur even without establishment of
BSE) as a result of importing from
Canada the bovine commodities
considered in this rule is negligible, is
not predicated on the eradication of BSE
in Canada.
Issue: One commenter indicated that
year-of-birth data collected by the EU
shows that, based on the number of BSE
cases detected in the United Kingdom
since 2001, there was a steady increase
in the number of BSE-positive cattle
born in the United Kingdom after its
1988 feed ban, beginning with cattle
born in the year 1990.
Response: We disagree with the
commenter. Since July 2001, when the
EU-wide active BSE surveillance
program commenced, an increasing
proportion of the total BSE cases in the
United Kingdom have been detected as
a result of targeted (active) surveillance
(DEFRA 2006b, figure 4.3). However, as
shown by the EC (EC 2006, chart B1),
the vast majority of BSE cases in the
United Kingdom were detected by
surveillance prior to 2001. Based on all
available United Kingdom BSE
surveillance data (DEFRA 2007), the
number of BSE cases in United
Kingdom birth year cohorts began to
decline in 1988, the year the initial
ruminant-to-ruminant feed ban was
introduced.
For the reasons discussed above, we
continue to consider it appropriate to
apply our estimates of BSE prevalence
in Canada to our risk assessment. As
noted above, we used two related, but
distinct, methods to estimate BSE
prevalence in Canada, and addressed
the uncertainty in the prevalence of BSE
in Canada by considering prevalence
estimates that differ by more than a
factor of five. Although we consider the
BSurvE Prevalence B estimate to be far
more likely to be true than is the BBC
estimate for the current standing
Canadian cattle population, we consider
the result of the BBC model as the more
likely prevalence estimate to apply to
the assessment of BSE risks associated
with imports from Canada over the next
20 years.
the feed ban was effectively enforced
(OIE Terrestrial Animal Health Code,
Chapter 2.3.13). We proposed to
consider March 1, 1999, as the date on
and after which a feed ban has been
effectively enforced in Canada. A
number of commenters addressed
Canadian enforcement of its feed ban,
and also addressed the date we
proposed to consider as the date of
effective enforcement of a feed ban in
Canada. Although some commenters
specifically supported March 1, 1999, as
the date of effective enforcement of a
ruminant-to-ruminant feed ban in
Canada, a number of other commenters
disagreed that Canada was effectively
enforcing a feed ban as of that date.
Some commenters suggested alternative
dates or time frames.
Issue: Several commenters stated that
APHIS’ determinations of the level of
compliance with the Canadian feed ban
and the time at which compliance was
achieved are arbitrary and scientifically
indeterminable.
Response: We disagree with the
commenters. In January 2005, USDA
sent a team to Canada to assess Canada’s
feed ban and its feed inspection
program to determine whether the
control measures put in place by the
Canadian Government were achieving
compliance with that country’s
regulations. APHIS conducted an
extensive review of the feed ban in
Canada. As part of its review, APHIS
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Feed Ban in Canada
As discussed above, in our January
2007 proposed rule, we proposed to
allow the importation of live bovines
from BSE minimal-risk regions if the
animals were born on or after a date
determined by APHIS to be the date on
and after which a ruminant-to-ruminant
feed ban in the region of export has been
effectively enforced. We noted that
experience around the world in
countries with BSE has demonstrated
that feed bans are effective control
measures, and that the incidence of BSE
worldwide continues to decline because
of these measures (OIE 2007a).
We indicated that, because of the
demonstrated efficacy of an effectively
enforced feed ban in reducing the
possibility of exposure of cattle to the
BSE agent, the OIE provides guidelines
for trade in live cattle from regions that
have reported BSE if such regions have
an effective feed ban in place, provided
the cattle were born after the date when
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The conclusion of our risk assessment
that, over the 20 years of the analysis,
the risk to the United States (i.e., the
likelihood of establishment and the
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analyzed CFIA’s description of past
cases of BSE in Canada, as well as
historical inspection and compliance
data related to the feed ban for the
previous 3 years, educational materials,
published notices, and the report of the
International Review Team that was
submitted to the U.S. Secretary of
Agriculture in February 2004.
Additionally, the U.S. team
accompanied the CFIA inspection staff
on inspections of randomly selected
commercial feed mills and rendering
facilities. At the facilities, the U.S. team
observed the application of the
inspection standards, observed
manufacturing techniques, and
discussed processes with facility
personnel involved in various steps of
feed manufacturing. In its report, the
team concluded that Canada has a
robust inspection program, that overall
compliance with the feed ban in Canada
is good, and that the feed ban is
reducing the risk of transmission of BSE
in the Canadian cattle population
(USDA 2005). The team’s findings
support our conclusions regarding the
level of compliance with the feed ban in
Canada.
Issue: In our January 2007 proposed
rule, in discussing our rationale for
considering March 1, 1999, to be the
date of effective enforcement of a feed
ban in Canada, we stated that a 12month period would generally be
sufficient to allow purchased feed
products that may contain MBM to be
completely used. One commenter
expressed uncertainty about that
estimation and suggested that it might
be advisable for APHIS to conduct a
quantitative assessment of compliance
with the feed ban to determine the date
of its effective enforcement.
Response: We recognize uncertainty
regarding the precise date on which
Canada achieved effective enforcement
of its feed ban, but we note that, given
the extremely low prevalence of BSE in
Canada along with the safeguards in the
United States, the impact on the overall
risk of a slightly earlier or later date
would be minimal. Although reducing
uncertainty can, at times, be achieved
by performing more rigorous
quantitative analyses, before attempting
to reduce the uncertainty regarding any
given factor or parameter—such as the
precise date on which Canada achieved
effective enforcement of its feed ban—
it is important to examine the
significance of the parameter to the
overall risk result.
Issue: Several commenters stated that
APHIS’ calculation of the amount of
time necessary for ruminant feed to
cycle through the Canadian feeding
system is irrelevant in the absence of
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effective enforcement of feed-ban
regulations in Canada. The commenters
stated that it was not until between 2000
and 2002 that Canada implemented
inspections of feed and rendering
facilities.
Response: The commenters’ statement
is not accurate. Inspections of rendering
facilities and feed mills in Canada began
immediately with the implementation of
the feed ban in that country in August
1997. Rendering facilities were required
to obtain an annual permit to operate,
and issuance of a permit required an
inspection of the facility. In addition,
CFIA immediately began a program for
inspection of commercial feed mills. All
commercial feed mills were inspected in
the first year after the implementation of
the feed ban, with none of the feed mills
found to be including prohibited
material in ruminant feed. Thereafter,
feed mills were on a 3-year inspection
interval until 2002, when annual
inspection of commercial feed mills was
initiated.
Issue: A number of commenters stated
that the diagnosis of BSE in cattle born
after the establishment of a feed ban in
Canada demonstrates that Canada’s feed
ban is either ineffective or not
effectively enforced.
Response: We disagree with the
commenters’ conclusion. The
commenters suggest that, in order for
the Canadian feed ban to be considered
effective, BSE surveillance data would
have to demonstrate that the likelihood
of BSE transmission in that country has
been eliminated. However, as noted in
our risk assessment, Canadian BSE
surveillance data do not provide a
statistical basis for distinguishing BSE
prevalence among birth year cohorts
(APHIS 2006b, p. 12); the overall
prevalence is so low that distinguishing
any difference is nearly impossible. In
other words, the data cannot distinguish
any significant difference in prevalence
among animals born in different years,
which would have been one way to
demonstrate the effect of a feed ban
(e.g., if the feed ban were implemented
at the beginning of 1997, surveillance
data showing a higher BSE prevalence
in animals born in 1996 than in animals
born in 1997 would support the
effectiveness of the feed ban). However,
in the absence of a feed ban that
reduced exposure to BSE, we would
expect the prevalence of the disease to
increase over time. We have no
evidence that such an increase has
occurred, but we do have data that the
feed ban is being enforced.
Furthermore, as we discussed in our
risk assessment, detection of BSE in an
animal born after the date a feed ban
was implemented does not indicate an
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overall failure of the measures in place
to stem transmission of the disease in
that country. Most other countries that
have experienced cases of BSE, have
reported similar cases. Of 25 countries
that have reported indigenous BSE
cases, only 4 reported no cases in 2005–
06 (OIE 2007). Human error is expected,
which is why the feed ban is comprised
of a number of interrelated measures
that have a cumulative effect. Our risk
assessment does not assume 100 percent
compliance with all measures all of the
time. We discussed factors related to the
feed ban in Canada since before its
implementation in 1997. We considered
activities related to inspection and
compliance with the feed ban, the
rendering industry, the risk of crosscontamination, education activities and
industry awareness, and on-farm
practices that might contribute to the
efficacy of the feed ban. In addition, we
highlighted the fact that since the
implementation of the feed ban on
August 4, 1997, CFIA has continued to
revise and strengthen its processes and
procedures to further enhance the
effectiveness of the feed ban. Canada’s
July 2007 modification of its feed ban to
remove SRMs from all animal feeds, pet
food, and fertilizer is a good example of
such enhancements. We concluded that
compliance with the feed ban measures
in Canada continues to increase as the
program evolves and that all of these
factors have resulted in a cumulative
reduction in the risk that Canadian
cattle will be exposed to the BSE agent.
Issue: Several commenters stated that
Canada cannot demonstrate that it has
effectively prevented the feeding of
ruminant material to cattle over the past
8 years. Commenters stated that eight or
nine Canadian feedlots were discovered
to still be feeding banned bone meal
products, and that, because of their
violations of the feed ban, 30,000
Canadian cattle were under quarantine.
Additionally, one commenter stated that
in March 2007, nine farms in
Saskatchewan and as many as 8,000
cattle, deer, and other ruminants were
quarantined after ruminant MBM was
accidentally shipped to those farms
from a Saskatoon feed mill. Another
commenter stated that, in December
2006, Canada’s Minister of Agriculture
and Agri-Food acknowledged that up to
10,000 head of Canadian cattle on 113
different farms in the Provinces of
Ottawa and Quebec had recently been
fed feed contaminated with ruminant
material.
Response: APHIS is aware of the
incidents reported in late 2006 and in
March 2007 and considered such
incidences very carefully in its
evaluation of the effectiveness of the
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feed ban. However, it is not clear to us
what the commenters are referring to
regarding 30,000 Canadian cattle under
quarantine.
It should be noted that the use of the
term ‘‘contaminated’’ above refers to the
potential inclusion in ruminant feed of
MBM derived from ruminants, but not
to the feeding of known BSEcontaminated material to ruminants.
Feed control systems, including those in
the United States, are inherently subject
to human error such as occurred in
these incidents. These compliance
errors require follow up and correction
by CFIA, just as in the United States
such incidents would necessitate
follow-up by the U.S. Human Health
and Services, Food and Drug
Administration (FDA). Following
detection of these occurrences, CFIA
conducted a detailed investigation and
traced all potentially contaminated feed.
CFIA accounted for and disposed of all
feed that did not enter the distribution
channels, and feed already distributed
to farms was removed, disposed of, and
replaced. CFIA conducted risk
assessments to help evaluate the
possibility that new cases of BSE would
occur due to the contamination of feed
with prohibited material, and concluded
that the overall risk was negligible. Even
though this finding indicated that it was
highly unlikely that animals exposed to
the involved feed would develop BSE in
the coming years, in those instances
where exposure to the feed could not be
ruled out, the CFIA has excluded these
animals and their meat and byproducts
from export eligibility. This measure
was established to meet the technical
requirements of various trading partners
and does not affect the movement or
marketing of these animals within
Canada. These findings, together with
Canada’s rapid and comprehensive
response to the incidents, reinforces our
confidence in the effective enforcement
of Canada’s ruminant feed ban.7
Issue: Some commenters questioned
the effectiveness of Canada’s feed ban,
given evidence of contamination of
ruminant feed with MBM derived from
ruminants. One commenter stated that,
in the five cases of cattle born after
March 1, 1999, where investigations of
BSE in Canadian cattle have been
completed, the reported cause of BSE
infectivity centered on ruminant MBM
used in non-ruminant feeds cross7 In the rulemaking for our 2005 final rule
establishing criteria for recognition of a region as a
BSE minimal-risk region, we discussed in detail our
evaluation of Canada’s veterinary infrastructure;
disease history; practices for preventing widespread
introduction, exposure, and/or establishment of
BSE; and measures taken following detection of the
disease (APHIS 2005).
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contaminating ruminant feeds, either
during processing at the feed mill or
during transport. Given that four
animals were born after March 1, 1999,
the commenters indicated that great care
must be given to the analysis of these
animals in the risk assessment and did
not feel that APHIS thoroughly
examined the cases.
Response: We agree with the
commenters that the investigations of
BSE in animals born in Canada in 2000
and 2002 suggest that these animals
were most likely exposed during their
first year of life to feed contaminated
during processing (CFIA 2006a). Reports
of the investigations identified incidents
of concern in which ruminant feed was
processed or transported immediately
following the handling of nonruminant
feed containing prohibited material.
Such incidents were in contravention of
Canadian regulations, which require
flushing and/or clean-out between
batches if ruminant feed is processed on
the same lines as feed containing
prohibited material.
We considered the issue of crosscontamination and concluded that
Canada has implemented measures to
prevent cross-contamination of
ruminant feed with prohibited materials
in the rendering and feed manufacturing
industries are essential for
implementation of an effective feed ban.
We also considered other factors—
including the regulatory actions taken to
implement the feed ban, education and
industry awareness efforts, inspection
and compliance activities, and on-farm
feeding practices—in our overall
evaluation to determine the date the
feed ban was effectively enforced in
Canada and, based on those factors,
identified March 1, 1999 as the date of
effective enforcement of the feed ban.
APHIS did not specifically address
each individual case of BSE in Canada
in the risk assessment, as the available
details of each epidemiological
investigation did not contribute to the
overall risk estimation. The risk
estimation was based on consideration
of all factors relevant in the risk
pathway. These included consideration
of the current Canadian feed ban, with
explicit recognition that cases born after
the feed ban was implemented in
August 1997, or after the March 1, 1999
date have occurred and could continue
to occur. The prevalence estimate
acknowledges that BSE is present in
Canada, albeit at a very low level. The
risk reduction factors in the United
States, including feed ban regulatory
activities similar to those in Canada,
were considered in the exposure
assessment. The combination of all of
these factors, including recognition that
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53329
human error can occur in any step of the
pathway, supported the conclusion that
the risk to the United States of BSE—i.e,
the likelihood of establishment and the
potential impact of cases that may occur
even without establishment—as a result
of importing from Canada the bovine
commodities considered in this rule is
negligible.
Issue: One commenter stated that
Canada has experienced an increase in
the number of BSE cases since it
instituted a feed ban in 1997.
Response: It appears that the
commenter is equating the number of
detected cases of BSE with the number
of infected animals in a national herd.
However, an increased number of
detections of BSE does not necessarily
mean an increase in prevalence. A BSE
detection rate is dependent not only on
prevalence, but also on intensity of
surveillance. An increased number of
BSE cases have been detected in Canada
as that country has increased
surveillance for the disease. As noted
above, an APHIS analysis of the
Canadian BSE surveillance data did not
find a statistical basis for distinguishing
BSE prevalence among birth year
cohorts.
Issue: A number of commenters
referred to the number of BSE cases in
cattle born in Canada after March 1,
1999, as evidence that the date should
not be accepted as the date of an
effectively enforced feed ban.
Commenters requested that APHIS
reassess the proposed rule in light of
recent diagnoses of such cattle.
Response: In the assessment of
potential BSE risk we conducted for this
rulemaking, we concluded that there is
an extremely low likelihood that cattle
born in Canada on or after March 1,
1999, will have been exposed to BSE.
This conclusion does not mean that
effective enforcement necessarily equals
no instances of contravention of the feed
ban, either accidentally or intentionally,
just as isolated transgressions of U.S.
laws do not necessarily constitute
ineffective enforcement of those laws.
While specific incidents of crosscontamination can, and most likely will,
happen, since no regulatory effort can
ensure 100 percent compliance, the
detection of BSE in several bovines in
Canada born after March 1, 1999 does
not negate the overall effect of the feed
ban in decreasing the opportunities for
transmission of disease. Empirical
evidence from the United Kingdom has
demonstrated, and simulation studies
have reinforced, that implementation of
a ruminant-to-ruminant feed ban leads
to continued decrease in prevalence
over time (Cohen, et al., 2001; 2003;
DEFRA 2006, EC 2003; 2005). Similar
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effects of a feed ban have been seen in
other countries in the EU, where there
have been continued detections of BSE
in cattle born after a feed ban is initially
implemented. At the same time,
however, the apparent number of cases
of BSE identified in the EU–15 Member
States has decreased every year since
2001. The available evidence leads
firmly to the conclusion that animals
born after the date of implementation of
a ruminant-to-ruminant feed ban are far
less likely to be exposed to the BSE
agent (Heim and Kihm, 2003).
Issue: A number of commenters
recommended various alternative dates
or timeframes for consideration as the
date of effective enforcement of a feed
ban in Canada. Most of the commenters
who recommended an alternative date
expressed concern regarding the
detection of BSE in bovines born in
Canada after March 1, 1999.
The recommended alternative dates or
timeframes included the following: July
1, 2007; the date of birth of the youngest
bovine in Canada that has been
determined to be BSE-positive; May 1,
2002; 5 to 7 years after the most recently
diagnosed case of BSE in Canada;
whenever Canada can verify 100 percent
compliance with its ruminant-toruminant feed ban; a staggered system of
dates that would increase the allowable
age of bovines intended for importation
from Canada as time progressed with no
additional diagnoses of BSE in Canada.
Some of the commenters who
suggested July 2007 as the date of
effective enforcement based their
recommendation on the fact that on July
12, 2007, Canada expanded its feed ban
to prohibit the inclusion of SRMs in any
animal feeds, pet foods, or fertilizers.
One commenter asked how APHIS can
be satisfied that the United States would
be importing a safe product if Canada
itself was not satisfied with the
safeguards in place at the time the
proposed rule was published, and
subsequently took additional measures
to strengthen its feed ban. A number of
commenters recommended that the
provisions of the proposed rule not be
implemented until Canada bans all
feeding of animal material to food
animals. One commenter stated that July
2007 would be an appropriate point to
begin the importation of breeding
animals that have had exposure to
processed animal feed, and that March
1, 1999 would be an acceptable date for
bovines that have not been exposed to
processed animal feeds—such as bison
maintained by Parks Canada.
Several commenters, who expressed
no animal health concerns with
identifying March 1, 1999 as the date of
effective enforcement of a feed ban in
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Canada, recommended that APHIS
consider harmonizing the date chosen
with the date Canada has identified as
the effective date of a ruminant-toruminant feed ban in the United States,
January 1, 1999.
Response: In prior rulemaking (APHIS
2005), we evaluated evidence
(regulations in place based on statutory
authority, adequate infrastructure to
implement the regulations, and
evidence of implementation and
monitoring) in making the
determination that compliance with the
feed ban in Canada is good and
concluded that the feed ban was
effectively enforced. In our process of
identifying the date of effective
enforcement of a ruminant-to-ruminant
feed ban in Canada, we considered
Canada’s implementation guidance and
policies. For example, we considered
the allowance of grace periods for
certain aspects of the industry, in
determining the practical
implementation period for the feed
regulations. Then we considered a
sufficient time period subsequent to this
implementation period to allow most
feed products to cycle through the
system, given the management practices
in the country. We concluded, based on
the above evaluations, that cattle born in
Canada on or after March 1, 1999, can
be imported into the United States with
an extremely low likelihood that they
have been exposed to the BSE agent.
As noted, a number of commenters
recommended that APHIS consider July
2007, when Canada expanded its feed
ban, as the date of effective enforcement
of the Canadian feed ban. We consider
the July 2007 expansion of the Canadian
feed ban to be an enhancement of an
already effective ban. CFIA, in
explaining its rationale for the enhanced
ban, emphasizes that, although
surveillance results and investigations
of BSE cases indicate that the feed ban
in Canada has effectively reduced the
spread of BSE since being implemented
in 1997, even compliance with the ban’s
requirements left limited opportunities
for contamination during manufacture,
transportation, and storage that CFIA
considered worth eliminating. In
addition, the accidental misuse of feed
on farms with multiple species could
not be discounted. With the enhanced
ban, CFIA projects that the eradication
of BSE in Canada will be accelerated.
Following such a regulatory path does
not indicate that the feed ban in Canada
prior to July 2007 was not effective or
effectively enforced.
With regard to the recommendation
that the date of effective enforcement of
the Canadian feed ban be identified as
the date of birth of the youngest bovine
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in Canada that has been determined to
be BSE-positive, we do not consider
such a change to be necessary or
justified. The risk assessment we
conducted for this rulemaking
acknowledged that BSE exists in Canada
and that there would likely be
additional cases detected. March 1, 1999
was never intended to be an absolute
cut-off point after which no new cases
of BSE would be acceptable. The risk
assessment concluded that, despite the
likelihood of additional diagnoses of
BSE in Canadian cattle, the proposed
amendments would pose negligible risk
to animal health and food safety in the
United States. If an infected cow were
to be imported into the United States, a
series of strong safeguards would have
to fail—in sequence—for that animal to
pose any risk.
With regard to the recommendation
that APHIS harmonize its identification
of the effective enforcement date of a
Canadian feed ban with the date
identified by Canada as the date of
effective enforcement in the United
States, we do not agree that such a
change would be appropriate or
necessary. APHIS arrived at the March
1, 1999 date for effective enforcement of
the feed ban in Canada by considering
not only the date the feed ban was
established in that country but also
information provided by Canada
regarding its implementation timetable,
as well as feeding practices in that
country. It does not necessarily follow
that implementation events in the
United States followed precisely the
same track as those in Canada.
Issue: In our January 2007 proposed
rule, we discussed the diagnosis of BSE
in cattle in Canada born after March 1,
1999, and stated that ‘‘such isolated
incidents are not epidemiologically
significant and do not contribute to
further spread of BSE, especially when
considered in light of the entire risk
pathway and its attendant risk
mitigations.’’
Several commenters took issue with
APHIS’ description of the cases as
‘‘isolated.’’ Some commenters stated
that ‘‘isolated’’ implies a solitary or
separated condition, which cannot be
said of the BSE cases recently confirmed
in Canada. Further, other commenters
stated the cases are linked by a trend in
geographic location, with the last three
cases occurring in the Province of
Alberta. One commenter stated that of
the nine cases of BSE detected in
Canada, four occurred in cattle born
after March 1, 1999, and that four of
nine cases—or 44 percent—do not
represent isolated cases and strongly
disagreed that this date corresponds to
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when Canada’s feed ban became
effectively enforced.
Response: We disagree with the
comments, although we acknowledge
that the term ‘‘isolated’’ could be
interpreted in several ways. The use of
the term in our proposed rule was not
intended to imply that the cases were
‘‘solitary or separated.’’ Our use of the
term ‘‘isolated’’ was intended to
characterize the cases as being small in
number and not indicative of a systemic
failure of the feed ban in Canada, but
rather the result of individual instances
of error in contravention of the feed ban
(e.g., inadequate cleaning between
handling of feed for non-ruminants and
feed for ruminants).
For the reasons discussed above, we
consider our determination that March
1, 1999 be deemed the date of effective
enforcement of the feed ban in Canada
to be reasonable, grounded firmly in the
regulatory basis and operations of the
ban in Canada, and entirely consistent
with the science and with OIE
guidelines. Accordingly, we are making
no changes based on the comments.
Likelihood of Exposure of Cattle in the
United States to BSE
The assessment is designed to
estimate the likelihood of each of the
multiple steps. Although we analyzed
the likelihood of each individual step in
the process occurring, we interpreted its
significance in the context of the entire
process.
As part of the risk assessment we
conducted for our January 2007
proposed rule, we evaluated both the
likelihood of ‘‘release’’ of the BSE agent
into the United States and the
likelihood of susceptible animals being
exposed, given such release. We
evaluated the pathways by which
infected Canadian cattle, if imported,
might expose U.S. cattle to BSE, and the
likelihood that these pathways might
lead to the establishment of the disease
in the U.S. cattle population.
Several steps must take place for BSE
to be transmitted to cattle in the United
States from a bovine imported live from
another country. A BSE-infected bovine
must be imported into the United States;
the infected bovine must die or be
slaughtered; tissues from that animal
that contain the infectious agent must be
sent to a rendering facility; the
infectivity present in these tissues must
survive inactivation in the rendering
process; the resulting meat-and-bone
meal (MBM) containing the abnormal
prion protein must be incorporated into
feed; and this feed must be fed to cattle
at a level adequate to infect the cattle.
(The amount of infectious material
required in feed for cattle to become
infected is dependent on the age of the
cattle; younger cattle are more
susceptible to BSE and require less BSEcontaminated feed to become infected
(Arnold and Wilesmith, 2004). We
indicated in our risk assessment that the
nature and likelihood of these pathways
depend in large part on mitigations
acting in series and in parallel that
reduce the likelihood that BSE will be
established in the United States.
A number of commenters addressed
the issues of the likelihood of release of
the BSE agent into the United States and
the likelihood of exposure of U.S. cattle
to BSE due to the importation of bovines
from Canada. In general, the
commenters said that we had
underestimated the likelihood of release
and/or exposure, or questioned one or
more elements of our assessment.
Issue: One commenter, whose
statements were referenced and
supported by a second commenter,
discussed the geographic distribution of
BSE cases in Canada and expressed
concern that Canada’s experience
demonstrates that certain locations in
the United States might be more
susceptible to BSE establishment than
others. The commenter stated that
events in Canada indicate that an
average risk estimate is meaningless for
BSE and demonstrates how ‘‘hot spots’’
(i.e., locations that are more susceptible
to spread of disease and, therefore, that
have a localized higher BSE prevalence)
allow BSE to propagate and spread. The
commenter stated that the model-based
53331
predictions in APHIS’ risk assessment
are useless because the models do not
account for geographic and other
sources of heterogeneity and pointed to
Alberta as a BSE hot spot. Further, the
commenter indicated that the APHIS
risk assessment has not provided any
real data or relevant analyses related to
BSE hot spot development and that
APHIS has not quantified the risks that
imports will create localized BSE hot
spots in the United States. The
commenter calculated that, if 5 percent
of U.S. locations are potential hot spots,
and 1 million animals are imported each
year with six of them BSE-positive, the
expected probability of at least one hot
spot being activated in the United States
is at least 77.7 percent.
Response: We disagree with the
commenters. The available evidence
provides no basis for distinguishing BSE
prevalence among Canadian provinces.
The commenter who singled out Alberta
provides no analysis to support the
hypothesis that the BSE prevalence in
Alberta is higher than in other
provinces. Through May 2007, reported
BSE cases have originated in three
western Provinces: Alberta (8 cases),
British Columbia (2 cases), and
Manitoba (1 case). No cases have been
reported through May 2007 in the
eastern Provinces. Intuition might
suggest that the BSE prevalence is
higher in Alberta. However, Alberta
contains approximately 40 percent of
the Canadian cattle herd. Other factors
being equal, BSE is more likely to be
detected in regions with large cattle
populations.
Apart from the detected cases,
geographically disaggregated data on
BSE surveillance and Canadian cattle
population demographics are not
available. However, assuming that the
total BSurvE points accumulated
through August 15, 2006 (APHIS 2006c,
table 4) were collected proportionally to
the cattle population size in each
province, table 3 presents the allocation
of the random sample size equivalents
(BSurvE points).
TABLE 3.—ALLOCATION OF BSURVE POINTS AMONG PROVINCES PROPORTIONAL TO HERD SIZE
Cattle
(000)*
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Province
Alberta ..........................................................................................................................
Manitoba ......................................................................................................................
British Columbia ...........................................................................................................
Saskatchewan ..............................................................................................................
Ontario .........................................................................................................................
Quebec ........................................................................................................................
Nova Scotia .................................................................................................................
New Brunswick ............................................................................................................
Prince Edward Island ...................................................................................................
Newfoundland ..............................................................................................................
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PO 00000
Frm 00019
Fmt 4701
Sfmt 4700
Percent
6,300.0
1,720.0
830.0
3,450.0
2,203.9
1,455.0
107.0
90.5
84.5
9.1
E:\FR\FM\18SER2.SGM
38.8
10.6
5.1
21.2
13.6
9.0
0.7
0.6
0.5
0.1
18SER2
BSurvE
points
BSE
cases**
594,858.4
162,405.8
78,370.2
325,755.8
208,096.6
137,384.0
10,103.2
8,545.2
7,978.7
....................
7
1
1
0+
0
0
0
0
0
........................
53332
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TABLE 3.—ALLOCATION OF BSURVE POINTS AMONG PROVINCES PROPORTIONAL TO HERD SIZE—Continued
Province
Cattle
(000)*
Percent
BSurvE
points
BSE
cases**
Labrador .......................................................................................................................
....................
....................
859.2
........................
Total ......................................................................................................................
16,250.0
....................
1,534,357
9
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*Source: Statistics Canada (2007).
**BSE cases reported through August 2006 were included in APHIS (2006c).
+The BSE case confirmed in May 2003 was born in Saskatchewan but reported in Alberta.
Based on this allocation of evidence,
a binomial likelihood ratio test (Fleiss et
al., 2003) fails to reject the hypothesis
that the provinces have the same BSE
prevalence. That is, the result provides
no basis for concluding that BSE
prevalence varies among provinces.
Depending on the method used to
estimate provincial BSE prevalence, the
test indicates that 11 to 20 BSE cases
would have to have been observed in
Alberta (or 4 to 7 cases in British
Columbia) before rejection of the
hypothesis.
The commenters provide no data or
analysis related to BSE hot-spot
development. APHIS’ risk assessment
discusses the apparent geographic
clustering of Canadian BSE cases
reported through August 2006 in three
western provinces: Alberta, British
Columbia, and Manitoba (APHIS 2006b,
pp. 12–13). (In addition, the May 2003
case reported in Alberta was born in
Saskatchewan.) However, APHIS also
noted that the Manitoba BSE case was
phenotypically different than the
previously detected BSE cases of
Canadian origin (APHIS 2006b). In
addition, in its risk assessment, APHIS
considered the CFIA report (CFIA 2006)
that discusses geographic and temporal
BSE clustering theories. APHIS
concluded that the detection of further
clusters (i.e., linked cases) that might be
defined in the future cannot be ruled
out and did not assume that any
Canadian provinces are BSE-free. While
BSE case investigations may reveal
associations among individual cases,
such as a common feed source, the
question of clustering is scale
dependent. At a local scale, there may
be associations between individual
cases, but at a regional or national scale,
the clusters themselves may be
geographically dispersed. In addition,
the geographic disease dispersal pattern
may change over time due to the
movement of cattle.
Further, the commenter provides no
evidence or analysis to support the
hypothesized sources of heterogeneity.
On the contrary, disaggregating the
available surveillance data into
numerous strata to account for
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hypothetical sources of heterogeneity
(geography, market class, etc.) generates
substantial uncertainty within strata by
diluting the sample size. One
consequence of this practice (commonly
called over-stratification) would be to
inflate the upper confidence level risk
estimates within putative strata (e.g.,
Alberta beef cattle).
With regard to quantifying the
likelihood of imports creating localized
hot spots in the United States, the
commenter provides no data or analysis,
and cites no existing scientific
literature, in support of the hypothesis
that some U.S. cattle-producing areas
are—on average—more susceptible than
others to the establishment of BSE.
While such spatial heterogeneity is
theoretically plausible, APHIS is
unaware of any empirical data that
would provide a statistical basis for
distinguishing BSE susceptibility among
U.S. cattle-producing locations.
Although the commenter claims that the
APHIS analysis represents an average
risk estimate, the assessment does
consider random variability on the
national scale in the BSE reproductive
rate (R0) and the number of infected
animals under each scenario or set of
assumptions (APHIS 2006b). In essence,
the commenter argues for a more
disaggregated risk model that has
random variability at the local level (in
which regions are assumed to vary
significantly from one another) rather
than at the national level, but the
comment does not provide any evidence
in support of the hypothesis that such
local differences (spatial heterogeneity)
either exist, can be distinguished from
a random distribution, or are of
sufficient magnitude that they need to
be accounted for by the model.
Finally, the commenter’s calculation
of a 77.7 percent probability of at least
one U.S. hot spot being activated rests
on two assumptions. First, the
commenter assumes that the prevalence
of BSE in Canada exceeds the APHIS
prevalence estimate by a factor of 10.
There is no evidence to support this
assumption. Second, the commenter
assumes that there is a 5 percent
probability that Canadian cattle would
PO 00000
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be introduced into pockets within the
United States where R0 exceeds unity.
(If R0 exceeds unity (one), the disease
will tend to spread. Conversely, if R0 is
less than unity, the number of cases will
tend to decline over time, and
ultimately the disease will die out.)
Other than asserting the existence of
such pockets and that 5 percent of U.S.
locations may be hot spots, the
commenter provides no evidence to
support this contention. Even if the
comment did provide such evidence, it
would have to show that in such
pockets the value of R0 substantially
exceeds 1 in order for there to be
evidence that a substantial impact is
likely. For example, if R0 = 1.1 and each
generation of the disease (i.e., the time
between infection of an animal and that
animal’s subsequent infection of another
animal) lasts just 2 years, it would take
40 years for the disease prevalence to
climb from 1 animal to 7. Finally, the
commenter’s suggestion supposes that
no action would be taken to address
vulnerabilities in a susceptible pocket if
BSE did materialize. This assumption is
inconsistent with APHIS’ policy and
record.
Issue: One commenter asked whether
the expected number of imported
animals by class (i.e., the intended use
of the animal, such as for breeding,
immediate slaughter, or feeding and
then slaughter) needed to be validated
or explored in the sensitivity analysis.
Response: We projected the expected
number of imported animals by class
because an animal’s usage will govern at
what age it goes to slaughter. How long
a bovine lives will, in turn, have an
effect on the animal’s likelihood of
developing detectable levels of BSE
infectivity. The projected numbers of
imports by age and use class used in our
risk assessment were prepared for
APHIS by USDA ERS. These values are
based on USDA baseline projections,
with specific factors considered based
on the regulatory changes proposed.
Additional details are provided in
Appendix 1 of the Regulatory Impact
Analysis and Final Regulatory
Flexibility Analysis.
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Although these estimates cannot be
entirely certain, they are based on the
input of experts in the fields of
commodity projection and cattle
markets iteratively refined with
estimates from widely accepted models.
Therefore, alternative plausible
assumptions for the number of imported
animals by class would not likely vary
substantially from those based on the
most current inputs. Hence, the import
projections do not contribute
significantly to uncertainty in the total
estimated rate at which BSE may be
introduced into the United States from
Canada. In any case, new economic
information based on market forces and
age verification described above
indicates that, compared to those used
in the published risk assessment, the
import projections should be revised
downwards, especially estimates for the
projected number of older cull animals.
As a result, any potential release of BSEinfected animals should be lower than
previously estimated. In addition, the
key determinant of the impact of an
introduction of BSE into the United
States is its propensity to spread within
the cattle herd. The risk assessment
results indicate that, because the
reproductive constant, R0, remains
consistently less than one, prevalence in
the United States will tend to fall over
time. (In order for the disease to spread,
R0 must exceed unity (one).)
Issue: One commenter stated that the
incidence rate among just the older
cattle covered by the proposed rule
would be expected to be even higher
than the overall incidence for all
Canadian cattle slaughtered, thereby
making the likely risk even greater.
Response: We are not certain what the
commenter is referencing as ‘‘overall
incidence for all Canadian cattle
slaughtered.’’ We note that APHIS
estimated the prevalence of BSE in the
standing adult cattle population in
Canada, not the BSE incidence in all
Canadian cattle slaughtered. The
Canadian BSE surveillance data provide
no statistical basis for concluding that
one birth-year cohort has a higher or
lower BSE prevalence than another.
Therefore, we assumed for our risk
assessment that all animals in the
current standing Canadian cattle
population, including animals 30
months of age and older that are eligible
for importation under this rule (as well
animals that are not eligible for
importation under this rule due to the
birth-date requirement) have the same
probability of BSE infection. However, it
would not be surprising if animals born
at an earlier date (i.e., either before or
around the time the feed ban was
implemented) have a greater likelihood
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of exposure to contaminated feed, and
therefore could have a higher
prevalence of BSE than animals born in
later years. For this reason, we are
restricting imports of live bovines from
Canada to those born after the date
when the country had an effectively
enforced feed ban—which we have
determined to be March 1, 1999.
Additionally, of the live bovines we
project will be imported following the
effective date of this rule, greater than
80 percent of the animals are expected
to be younger than 2 years of age at the
time of importation.8 Therefore, even if
older animals had some significantly
higher level of BSE prevalence (which is
already reflected in the standing herd
estimates), the fact that this rule
excludes the importation from Canada
of bovines born before March 1, 1999,
along with the fact that the large
majority of animals are expected to be
young, would tend to decrease, rather
than increase the overall risk from that
which we have estimated.
Issue: One commenter indicated that
Canada’s BSE prevalence rate
essentially guarantees (probability
greater than 98 percent) that some BSEpositive cattle will enter the United
States. Another commenter suggested
that there is a 99.75 percent chance that
one or more cattle that would test
positive for BSE will be imported into
the United States among the first
million cattle that would be imported
after adoption of the proposed rule.
Response: We note that prevalence
refers to the proportion of BSE-infected
animals, not the proportion of animals
that would test positive for BSE. BSEinfected cattle are unlikely to test
positive unless they are tested at a late
stage of disease incubation.
Nevertheless, the commenter’s
estimated likelihood of entry of BSEinfected cattle is consistent with the
APHIS risk assessment. The risk
assessment clearly acknowledged the
possibility of importing infected
animals. Given the estimated current
prevalence in Canada, table 7 in the risk
assessment presents the projections for
imports in the first year of
8 As discussed in the regulatory impact analysis
APHIS conducted for this rule, most steers and
heifers are ready for slaughter between 16 and 24
months of age, feeders are generally ready between
9 and 15 months of age, and vealers and light calves
are slaughtered between less than 3 months and 8
months of age. In our analysis, we project that the
total number of projected imports from Canada for
these three categories of cattle in 2008 will be
987,000. This represents about 88 percent of the
overall number of cattle projected to be imported
from Canada in 2008. This percentage does not
include imported replacement heifers and other
breeding stock younger than 2 years of age.
PO 00000
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53333
implementation, including infected
animals.
Issue: One commenter expressed
doubt regarding the conclusion reached
by the APHIS risk assessment that—
because Canada’s BSE prevalence will
likely decrease over time, and because
of the barriers to BSE transmission in
the United States—the likelihood of BSE
exposure and establishment in the U.S.
cattle population as a consequence of
the proposed rule is negligible. The
commenter stated that the overlapping
safeguarding measures described in the
risk assessment have not prevented the
continued spread of BSE in other
countries (including Canada) that have
relied on similar measures. The
commenter further suggested that the
measures have not been empirically
tested or validated and cited the four
Canadian BSE cases born in the years
2000 and 2002 as evidence that the
measures are, in fact, ineffective to
either reduce or prevent BSE infection.
Response: We disagree with the
commenter’s statements. Various data—
epidemiological, modeling, and
experimental—clearly demonstrate that
the barriers discussed in the risk
assessment and the proposed rule will
decrease the risk of the introduction of
BSE and its amplification. These
barriers have been used internationally
as strategies for the control and
prevention of BSE. Furthermore, the
barriers have demonstrated a striking
effect in curtailing the epidemic and are
responsible for the downward pressure
on the prevalence of BSE observed in
the United Kingdom and Europe. As
described in the risk assessment: (1)
Slaughter controls prevent the recycling
of infectivity into human food and cattle
feed; (2) rendering processes contribute
to the inactivation of the BSE agent; and
(3) feed controls prevent the recycling
into cattle feed. In addition, there is
epidemiological evidence of an agerelated susceptibility to infection, which
implies that the animal not only needs
to be exposed to the BSE agent to
become infected, but needs to be
exposed with a sufficient dose at the
time in its life that it is susceptible. For
disease transmission to occur, the
following events must happen in
sequence: An infected animal dies or is
slaughtered at a sufficiently late point in
the incubation period to have significant
infectivity present in certain tissues;
those tissues go into the rendering
system; some level of infectivity
remains after the rendering process; the
resulting protein is included in feed;
and feed is fed to a ruminant in a
sufficient amount at an age when it is
susceptible. Although this could occur,
the likelihood of it happening
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repeatedly is negligible. This fact is
demonstrated in the quantitative
exposure model used in our risk
assessment—i.e., transmission can
occur, but it is not sufficient to sustain
the disease (R0 remains far less than
one).
We reviewed Canada’s feed
production process (e.g., regulations in
place based on statutory authority,
infrastructure to implement the
regulations, and compliance with the
regulations). We used a peer-reviewed
model to estimate the prevalence and
determined that the prevalence in
Canada is extremely low. We also used
a peer-reviewed exposure model in our
assessment of the risk (Cohen et al.,
2001; 2003). This model takes into
consideration several parameter values
that are based on experimental and
epidemiological information related to
BSE. These parameters represent key
epidemiological elements related to the
mechanisms by which BSE is
transmitted. As we indicate in the
exposure assessment, that assessment
demonstrated that, because we expect
Canada’s prevalence to decrease over
time, and because of the barriers to BSE
transmission in the United States, the
likelihood of BSE establishment in the
U.S. cattle population is negligible. We
reach the same conclusion even without
assuming a drop in Canada’s BSE
prevalence over the next 20 years.
Issue: One commenter, in addressing
risk mitigation measures in place in the
United States, stated that several
loopholes remain in the U.S. feed ban
through which BSE infectivity could be
introduced to cattle, despite
recommendations from an APHIS TSE
Working Group.
Response: APHIS has proceeded in a
thorough and deliberative manner, in
cooperation with FSIS and FDA, to
determine the steps necessary to
continue to protect animal and public
health. APHIS has used a peer-reviewed
model to assess the likelihood of
exposure of cattle to BSE as a result of
importing live cattle from Canada under
the proposed rule (Cohen et al., 2001;
2003). This model takes into
consideration several parameter values
relevant to the cattle production
process, including what the commenter
refers to as loopholes in the feed ban
regulations. Even after considering these
features of the U.S. system, the results
indicate that the likelihood of BSE
exposure and establishment in the U.S.
cattle population as a consequence of
infectivity introduced via imports from
Canada is negligible.
Issue: One commenter stated that the
models that Canada and the United
States used in estimating BSE risk are
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not validated and have no predictive
value. The commenter stated further
that the predicted risks from the
Harvard model would increase almost
15-fold if compliance is less than
assumed in the base case.
Response: We disagree with the
commenter’s assessment of the
quantitative exposure model we used in
developing our risk assessment. As
noted earlier, the plausibility of the
model was established by comparing its
predictions for Switzerland against the
observed progression of BSE within that
country’s cattle herd (Cohen et al.,
2003). Although the model’s
performance in the United States has
not been empirically evaluated (because
there have been too few cases in the
United States to do so), the use of
models to characterize future risks is
well-accepted in the scientific
community.
The commenter cites an FSIS risk
assessment (Cohen and Gray, 2005),
which uses a version of the Harvard
model, to argue that, if the misfeeding
rate parameter is highly uncertain, the
resulting range of results generated by
the simulation model is likewise wide.
As explained in the APHIS risk
assessment, new information indicates
that the original range of estimates for
the misfeeding rate in the Harvard
model as originally developed in 2001
were overly pessimistic. APHIS
obtained new data and, using these new
data in the Harvard model, reduced the
range of the original estimates.
Therefore, in APHIS’ evaluation, the
impact of misfeeding on the output of
the model is much more modest.
Issue: One commenter asserted that
APHIS’ risk assessment model predicts
low or ‘‘negligible’’ risks only if
optimistic assumptions are made.
Response: APHIS disagrees with the
commenter. The commenter simply
cites the results of APHIS’ own
sensitivity analysis using ‘‘pessimistic’’
assumptions and provides no evidence
or analysis demonstrating that the
APHIS ‘‘base case scenario’’
assumptions are optimistic. APHIS
combined qualitative and quantitative
methods in its assessment of risk from
live cattle. We qualitatively evaluated
what we expect as the most likely
scenario—prevalence drops in Canada
over the next 20 years, resulting in
decreases in potential release and
exposure. While the commenter may
consider this expectation an optimistic
assumption, we do not and we note that
this assumption is based on evidence
from countries around the world that a
feed ban provides continuous
downward pressure on prevalence.
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However, APHIS also considered
other less likely (more pessimistic)
scenarios, for which we assumed that
the prevalence in Canada remained
constant over the next 20 years, using a
quantitative exposure model. The
quantitative exposure model simulates
the cattle management system in the
United States, with assumptions made
for certain variables, or parameters as
input to this system. These parameters
include BSE prevalence in Canada,
which is an exogenous variable (and
therefore, external to the U.S. system of
mitigations), and many endogenous, or
internal parameters. The endogenous
parameters include various aspects of
compliance with the FDA feed ban, how
many carcasses enter the rendering
system, what rendering processes are
used, how rendered protein is
incorporated into feed, and many other
factors that can contribute to the spread
of BSE. The values for each of these
parameters basic assumptions that are
meant to represent the most plausible
and realistic representation of the U.S.
system are reflected in the ‘‘base case
scenario.’’
Assumptions regarding those
parameters for which we have the least
information (or the most uncertainty)
were changed to more pessimistic, but
still plausible, values in the sensitivity
analysis, to evaluate the degree to which
these changes would affect the results as
compared to the base case. Given that at
least one significant parameter—the
constant prevalence of disease in
Canada—was pessimistic even in the
base case, we do not agree with the
commenter’s assertion that the
quantitative model predicts low or
negligible risk only if optimistic
assumptions are used. Moreover, even
under the more pessimistic scenario
examined in the senstivity analysis, the
reproductive rate of BSE (R0) remains far
below 1, indicating that the disease
would not become established in the
United States.
Issue: Several commenters stated that
APHIS has not adequately considered
the risk that imperfect compliance with
U.S. SRM removal policies would have
once we allow the importation of cattle
over 30 months of age from Canada. One
of the commenters stated further that
APHIS provided no data or analysis in
the proposed rule to address this series
of known incidences of noncompliance.
Response: We disagree with the
commenters. As noted in our risk
assessment, the quantitative exposure
model assumes that SRMs are
effectively removed 99 percent of the
time. This assumption is based on FSIS
summaries of Noncompliance Records
(NRs) performed from January 2004 to
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May 2005 in about 6,000 federally
inspected meat and poultry
establishments. Based on these records,
FSIS estimated that noncompliance
with respect to SRM-related regulations
had a frequency of less than 1 percent.
To explore the possible impact of
assuming an arbitrary decrease
(compared to the results of our exposure
model) in SRM removal compliance on
the availability of infectivity for human
consumption, we can discuss the
significance of an order of magnitude
increase in available infectivity
compared to our model’s findings. First,
we consider the results of that model,
which used the unlikely assumption
that prevalence in Canada (and thus the
proportion of infected animals imported
from Canada) remained constant over
the next 20 years. In the model’s
scenario, the total amount of infectivity
potentially available for human
consumption over the 20 years of the
analysis is 45 cattle oral infectious dose50 units (ID50s). (BSE infectivity is
expressed in terms of cattle oral ID50s.
A cattle oral ID50 is defined as the
amount of infectivity required to cause
infection in 50 percent of an exposed
cattle population (APHIS 2006)). The
significance of cattle oral ID50 units to
human exposure and susceptibility is
not known; however, various studies
suggest that the infectious agent may be
10 to 10,000 times less pathogenic in
humans than in cattle because of a
species barrier (EC SSC, 2000). Thus, if
the cattle—human species barrier were
100, it would mean that 100 times more
infective material would be required in
order to have a similar probability of
infecting a human as a bovine. Comer
and Huntly (2003) estimated, after an
evaluation of available literature, that 54
million bovine oral ID50 units were
available for human consumption in
Great Britain from 1980 to 2003. This
extremely large amount of available
infectivity has resulted in 165 cases of
vCJD identified in the United Kingdom
through April 2007, plus a few
additional cases identified in other
countries but attributed to exposure in
the United Kingdom. When compared to
the United Kingdom’s BSE experience
and the associated estimate of available
bovine oral ID50 units, the expected, or
average value of 45 cattle oral ID50
indicates that only a miniscule amount
of the BSE infective agent that could
possibly be available for potential
human exposure in the United States
over a 20-year period (APHIS 2006).
(The potential for human exposure
under this scenario is estimated at
1,200,000 times less in the United States
than what the United Kingdom
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experienced during its BSE epidemic.)
Even if compliance with the SRM ban
were not as high as the 99 percent
estimated in our exposure model, and
we were to assume that the infectivity
available for human consumption were
increased by an order of magnitude
(10x), it would still be far less than that
estimated to have circulated in the
United Kingdom and, we conclude, not
to be of significance to human health.
Issue: One commenter stated that,
although APHIS assumes that removal
of SRMs from a bovine carcass will
effectively shield consumers from
exposure to BSE, numerous studies have
demonstrated limitations on mitigating
the risk of BSE exposure via SRM
removal. In particular, the commenter
stated that APHIS did not appropriately
consider several studies (Buschmann,
2005; Iwamaru et al., 2005; Hoffman,
2006) related to the distribution of
SRMs, and that APHIS failed to explain
why these uncertainties and concerns
do not undermine its almost exclusive
reliance on SRM removal requirements
to protect American public health from
potentially hazardous Canadian
imports.
Response: We are aware of the studies
cited by the commenter and do not
agree that they question the efficacy of
SRM removal. We acknowledge that
studies using new methods that provide
increased sensitivity will probably
demonstrate the presence of PrPBSE (the
abnormal form of the prion protein) in
various tissues. However, demonstrating
the presence of PrPBSE does not
necessarily indicate the presence of BSE
infectivity, especially if no infectivity is
demonstrated via the most sensitive
method available: Cattle-to-cattle
exposure via intracerebral transmission.
Therefore, one cannot automatically
assume that a finding of PrPBSE in a
tissue means the tissue should be
defined as an SRM. The OIE made this
particular point in the Terrestrial
Animal Health Standards Commission
Report, October 2006—Supporting
Document for Chapter 2.3.13. Of the
Terrestrial Animal Health Code on
Bovine Spongiform Encephalopathy, as
follows:
The availability of experimental infectivity
data has significantly increased in recent
years. During the same interval, extremely
sensitive tests have been developed,
including those employing highly sensitive
transgenic mice strains and potentially more
sensitive laboratory PrP detection methods.
With the development of such highly
sensitive methods, the probability of
detection of PrPBSE in tissues that are not
currently listed as infectious is increasing.
However, such findings need to be
considered in context, and their relevance to
establishing risk to consumers evaluated
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carefully when the quantity of PrPBSE
detected is potentially below the limit of
detection of intracerebral (i.c.) cattle to cattle
bioassay. By April 2007, 165 variant
Creutzfeldt-Jakob Disease (vCJD) cases had
been detected in the United Kingdom, a
country where most probably the majority of
the population was exposed to the BSE-agent.
The latest models of the vCJD epidemic
estimate that the potential scale of the
clinical epidemic arising from food-borne
exposure is unlikely to exceed 400 future
cases in the United Kingdom (Clarke and
Ghani, 2005). The relatively low number of
predicted vCJD cases in relation to the
massive exposure to the BSE agent is
suggested to be due mainly to a significant
species barrier between cattle and humans
(Comer and Huntley, 2004; Bishop et al.,
2006).
APHIS is familiar with the results of
the study (Buschmann, 2005) cited by
the commenter in which tissues from a
BSE-diseased cow were inoculated into
genetically engineered (transgenic) mice
that are highly susceptible to BSE and
which over-express the bovine prion
protein. Using this extremely sensitive
mouse assay, this study demonstrated
low levels of infectivity in the
peripheral nervous system (e.g., facial
and sciatic nerves) of the infected cow.
APHIS discussed these findings in its
risk assessment and concluded that
‘‘[g]iven all these factors there is not
sufficient information to alter our
understanding of the epidemiologically
significant distribution of BSE
infectivity in cattle.’’ APHIS also
acknowledges the results of Japanese
studies in which PrPBSE has been
reported in the peripheral nerves of a
case of BSE (Iwamaru et al., 2005) and
in some peripheral nerves of cattle
slaughtered at abattoirs in Japan (Iwata
et al., 2006) by Western blot analyses.
APHIS has also reviewed the German
study in which infectivity was detected
in the brainstem of an animal at 24
months post-infection (Hoffman, 2006).
We have carefully considered all of
these findings. USDA reviews and takes
into consideration all BSE research for
the definitions of SRMs, as does Canada
and other countries internationally. As
noted in the quote above, international
policies regarding SRM removal have
not changed based on the results of the
studies discussed. Both the U.S. and
Canadian policies regarding SRM
removal are consistent with
international standards.
Issue: One commenter referenced an
FSIS study that found that the removal
of SRMs can reduce human exposure to
BSE by about 80 percent. The
commenter stated that this level of
protection is clearly inadequate to
protect the United States from risks
associated with the importation of older
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cattle from Canada that represent an
inherently higher risk for BSE. The
commenter then referred to the
sensitivity analysis APHIS conducted as
part of its risk assessment, which
incorporated a higher value for Canada’s
BSE prevalence than in the more likely
base-case scenario. The commenter
expressed concern that the sensitivity
analysis revealed that 108 BSE infected
cattle could be imported into the United
States over the next 20 years and result
in 12 new BSE cases in the United
States.
Response: We disagree with the
commenter regarding the significance
and applicability of the cited study. In
this response, we present a more
appropriate study from which to draw
useful inferences regarding the impacts
of SRM removal.
The 2004 FSIS document referred to
by the commenter—Preliminary
Analysis of Interim Final Rules and An
Interpretive Rule to Prevent the BSE
Agent From Entering the U.S. Food
Supply’’—is an analysis intended to
evaluate the major impacts of measures
contained in the FSIS interim final rules
published and implemented in January
2004. FSIS used the Harvard model in
this analysis to estimate the benefits of
these measures, specifically ‘‘those
[benefits] resulting from the reduction
in human exposure to BSE infectivity.’’
FSIS used this model to create a
baseline estimate of potential human
exposure and then evaluated three
scenarios of risk mitigation options (e.g.,
SRM removal) for comparison to the
baseline. In each simulation, FSIS
assumed that five infected animals were
introduced into the United States in
2003, and then simulated the spread of
BSE infectivity until 2020. The
simulations of the risk mitigation
measures were run assuming that the
mitigations were implemented in 2004,
i.e., approximately 12 months after the
introduction of infected animals. While
the commenter is correct that this
analysis demonstrated a reduction in
potential human exposure of 80 percent,
the comment does not accurately
portray the context of this result. Given
the assumptions used in the simulation
(i.e., the risk mitigation measures,
including SRM removal, were not
implemented until 12 months after
introduction of infectivity), a certain
amount of infectivity would have
become available for human exposure
before the mitigations measures were
implemented in the model scenario.
Therefore, the mitigation measures
could never eliminate all of the
infectivity available. Since all scenarios
included at least some time in which
the mitigations were not implemented,
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under the simulations, a certain amount
of potential infectivity was allowed into
inappropriate channels, such as human
food. Because none of these scenarios
incorporated the more realistic
assumption that the mitigations were
implemented (even imperfectly)
throughout the simulation period, it is
inappropriate to use this analysis as a
citation for the level of public health
protection provided by risk mitigation
measures in place in the United States.
A more appropriate analysis for
understanding the role of SRM removal
in potential human exposure to BSE
infectivity would be the FSIS update of
the same Harvard simulation model that
was available for public comment in
2006. APHIS cites the analysis in the
risk assessment conducted for this
rulemaking as Cohen and Gray (2005).
This updated model used the ‘‘base
case’’ as the circumstances in the United
States prior to December 2003, and
simulated the response of the U.S.
system for 20 years following the import
of BSE-infected cattle. FSIS’ updated
model estimated the impact of various
risk management measures, including
measures that were adopted,
considered, or proposed by various
agencies and groups. These simulations,
where the risk mitigation was applied
during the entire simulation, as opposed
to the simulation in the analysis cited
by the commenter (in which it was not),
indicated that removing SRMs, as
currently defined by FSIS, reduced
potential human exposure by more than
99 percent, on average. This report also
stated that ‘‘[i]t is worth noting that
these measures reduce what is already
a small exposure in absolute terms.’’
Issue: One commenter stated that
SRM removal requirements have not
been in place long enough for an effect
to be determined, due to the
exceedingly long incubation periods
assumed for humans. The commenter
stated further that the experience of
other countries in which BSE has been
detected (except for Canada) cannot be
used to demonstrate that SRM removal
is highly effective, because other
countries have more stringent SRM
removal requirements than do Canada
and the United States and their
experience is not applicable for
predicting risk in the United States.
Response: The commenter appears to
be questioning two points—first,
whether SRM removal is actually highly
effective in protecting public health,
and second, whether experience in
Europe can be used as a comparison for
expectations in North America.
The commenter is correct in that there
has been no specific controlled study
that clearly and unequivocally
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demonstrates the effectiveness of SRM
restrictions on protecting public health.
The absence of such a study does not
negate the fact, however, that
substantial epidemiological and case
evidence clearly indicate the success of
such control measures. It is widely and
generally accepted internationally,
including by such international bodies
such as the World Health Organization
(WHO) and the OIE, that the primary
public health protective measure
regarding BSE is the removal of SRMs
from the human food supply (WHO,
2002).
The OIE Scientific Revue notes the
following: ‘‘Excluding SRM from the
human food chain effectively minimizes
the risk of human exposure and is the
most important measure taken to protect
consumers. Failure to remove SRMs
would probably expose a large number
of consumers to an unnecessary risk.’’
(Heim and Kihm, 2003). This point is
also widely acknowledged in scientific
literature, including articles cited by the
commenter. For example, Bradley and
Liberski (2004) conclude that ‘‘risks to
humans from infected cattle are now
remote so long as the [bans on the use
of SRMs in human food] are rigorously
enforced.’’ Fox and Peterson (2004)
conclude that ‘‘[a]doption of the human
[specified bovine offal] ban in the
United Kingdom in 1989 is probably the
only example in the BSE story of a
government going beyond expert
opinion in taking a precautionary
measure. It turned out to be the correct
decision, and likely saved thousands of
people from exposure to the disease.’’
Simulation models and analysis
conducted in the United Kingdom
support the assumption that primary
exposure sources for people were SRMs
in the food supply prior to imposed
restrictions. These models have been
updated and revised repeatedly since
the original identification of vCJD and
the link to BSE in cattle (Ghani and
others, 1998, 2000, 2001, 2003, 2005).
They incorporate assumptions for all the
parameters that could influence the
course of vCJD in the United Kingdom—
including assumptions about primary
exposure from dietary sources,
calculations about how many infected
cattle may have been slaughtered at
different points in time, what tissues
from those animals were available for
consumption, and what restrictions
were imposed on the tissues and types
of products available for consumption.
The models are updated routinely to
incorporate new information about vCJD
cases as they are reported.
These models have been used to
predict the course of the vCJD epidemic
in the United Kingdom. Initially, the
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projections were fairly high with
considerable uncertainty. As more
information is incorporated into the
models, these projections continue to
decline and the uncertainty levels also
decrease. The number of clinical cases
of vCJD in the United Kingdom has
continued to decline since an apparent
peak in 2000 (Andrews, 2007). This
decline is consistent with projections
made from the models, thus validating
some of the assumptions used in the
models. As an example, Cooper and
Bird (2003) assume that the primary
sources of exposure are the
consumption of meat products—
including mechanically separated meat
and head meat—that were most likely
contaminated with SRMs such as spinal
cord, dorsal root ganglia, and brain.
Restrictions on the inclusion of spinal
cord and brain, among other tissues,
were initially imposed in the United
Kingdom in 1989. Restrictions on the
production of mechanically separated
meat, which included a significant level
of infectivity from dorsal root ganglia,
were imposed in the United Kingdom in
1995. Cooper and Bird (2003) concluded
that ‘‘[t]here is remarkable similarity
between the age distribution and gender
of simulated and observed vCJD
patients, which supports (but does not
prove) our assumption about the
primary sources of exposure to BSE.’’
The commenter notes the
‘‘exceedingly long incubation periods
assumed for humans.’’ More recent
updates of the models described
previously have included estimates of
the mean incubation period for vCJD
(Ghani et al., 2003) and estimated the
mean incubation period for vCJD at 12.6
years when using the accumulated case
data from confirmed vCJD cases. When
additional information was added from
results of a screening study performed
on appendix and tonsil tissues, the
mean incubation period was 16.7 years
when fitted to this data. From this
evidence, we can conclude that even the
longer mean incubation period of 16.7
years would allow sufficient time to
demonstrate the effect of SRM
restrictions on the outbreak, since the
initial SRM restrictions were imposed in
1989. We note that all vCJD cases that
have been genotyped to date, with one
exception, have been of the homozygous
methionine (MM) genotype at codon
129 of the human prion protein gene. It
is estimated that approximately 40
percent of the Caucasian population is
homozygous methionine, with
approximately 10 percent valine
homozygous, and the remaining 50
percent heterozygous. While the effect
of genotype on vCJD is still unknown,
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we can evaluate scenarios in the MM
genotype as an example of epidemic
progression, because this genotype may
be the most susceptible and/or have
shorter incubation periods than other
genotypes.
The second point the commenter
raises is whether there would be
significant differences in potential
public health exposure due to the
different definitions of SRMs in Europe
and North America (Canada and the
United States). While these definitions
identify essentially the same tissues,
European regulations define tissues
such as brain and spinal cord as SRMs
in animals greater than 12 months of
age, where North American regulations
define these tissues as SRMs in animals
greater than 30 months of age.
In the past few years, significant
consideration has been given to the age
limits on SRMs and their
appropriateness. Additional information
obtained from new research findings has
contributed to these evaluations.
Scientists in Europe have specifically
examined these findings as part of their
consideration on the age limit in cattle
for the removal of SRMs (EFSA, 2005;
2007). In each of these opinions, they
conclude that any likely detectable
infectivity in the central nervous system
(CNS)—including the SRMs in
question—appears at about 75 percent
of the incubation time. These opinions
also note that the experimental low-dose
scenarios are more likely to resemble
the actual field exposure. The low-dose
research scenarios are those in which
calves were exposed orally to 1 gram of
highly infective brain tissue, rather than
the 100 grams used in the high-dose
scenario. Experimental attack rate
studies indicate that the incubation
period for the low-dose scenario has a
mean of 60 months, with a range of 45
to 73 months (Wells et al., 2007). Using
the low end of this range of incubation
period, and assuming that infectivity is
present in the CNS at 75 percent of the
incubation period, they predict that
infectivity would be sub-detectable or
still absent in CNS in cattle aged 33
months.
In the United Kingdom, even
including cases from the height of the
BSE epidemic there, which are believed
to have had shorter incubation periods
than more recent cases, the peak age at
onset of clinical signs was 5 to 6 years.
This age of clinical onset is consistent
with an assumption that the average
incubation period in the United
Kingdom has been about 60 months.
The average age of animals identified
with disease in the EU is higher than
this—the average was 86 months in
2001 and has increased since then. This
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53337
evidence indicates that considering
certain tissues in bovines 30 months of
age or older to be SRMs, and removing
and disposing of those tissues, would
eliminate the majority of infectivity
present, and removing and disposing of
these same tissues from bovines
between 12 and 30 months of age would
not provide any significant additional
protection.
This same point is illustrated in
various models. Comer and Huntly
(2003) modeled the potential human
exposure available in the United
Kingdom from 1980 through 2002. They
concluded that an estimated total of 54
million bovine oral ID50 units could
have been consumed in that timeframe.
This period included both the beginning
of the epidemic in cattle, before the
disease was recognized and public
health control measures were
established, and later in the epidemic
when control measures were developed
and instituted. Comer and Huntly also
concluded that 99.4 percent of this
estimated exposure was from animals
older than 30 months of age. Therefore,
SRM restrictions from animals greater
than 30 months would reduce the vast
majority of potential exposure.
In summary, we are in agreement with
the conclusion that has been widely
reached and that has generally been
accepted internationally, that the
primary public health protective
measure regarding BSE is the removal of
SRMs from the human food supply.
Issue: One commenter stated that
APHIS’ assertion that the rendering
process is important in the inactivation
of the BSE agent is overstated.
Response: As we stated in our January
2007 proposed rule, we recognize that
standard rendering processes do not
completely inactivate the BSE agent,
and that rendered protein such as MBM
derived from infected animals may
remain contaminated. However, the
rendering process is an important factor
in BSE risk reduction for two reasons.
First, standard rendering processes
will inactivate significant levels of any
BSE infectivity that might remain in
materials sent to rendering by subjecting
the material to intense heat and
pressure. The risk assessment
conducted for this rulemaking noted
that the rendering process has proven to
be effective in reducing the level of
infectivity. This is based on data
regarding inactivation by various
rendering methods (Taylor et al., 1995;
Taylor et al., 1997). The assumptions on
this point used in the quantitative
exposure model have been previously
explained (Cohen et al., 2002, 2003) and
include a range from 0 logs reduction in
infectivity in a vacuum rendering
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system to 3.1 logs reduction in a batch
system. The proportions of cattle
rendered in the various systems were
also explained, with the majority of
rendering (90 percent) done in either a
continuous/fat-added system (providing
a 2.0 log or 99 percent reduction) or a
continuous/no-fat-added system
(providing a 1.0 log or a 90 percent
reduction). On average, the rendering
process inactivates 1.4 logs of
infectivity, or greater than 97 percent.
Additionally, rendering serves as a
critical control point in redirecting
ruminant proteins away from cattle
feed. In the risk assessment we
conducted for this rulemaking, we
explained that the rendering process
will contribute to the prevention of BSE
as part of a series of sequential barriers,
rather than as an independent barrier.
Issue: One commenter expressed
concerns about plate waste as a
potential pathway for BSE infection of
U.S. cattle, because the proposed rule
did not prohibit the feeding of plate
waste, including beef, to cattle. The
commenter referred to APHIS’ risk
analysis that accompanied the
rulemaking related to the importation of
boneless beef from Japan (70 FR 73905–
73919, Docket No. 05–004–2), which
concluded that the plate-waste pathway
did not present a significant BSE risk,
and stated that the conclusion reached
in that risk assessment would not be
applicable regarding beef from Canada,
because the expected amount of product
from Canada would be much greater
than that projected for importation from
Japan.
Response: We do not agree with the
commenter that plate waste is a
potentially significant BSE pathway due
to this rule. In the risk analysis we
conducted for the rule related to the
importation of boneless beef from Japan,
we discussed direct and indirect
exposure pathways by which such beef
might expose U.S. cattle to BSE if the
product contained the BSE agent. In
addition, we stated in unequivocal
terms that the primary factors limiting
the likelihood that whole cuts of
boneless beef imported from Japan
would expose the U.S. cattle population
to BSE are (1) the inherently low risk of
the product, (2) measures to prevent
contamination, which would be the
same for any beef from cattle from
Canada that might become plate waste,
and (3) the fact that the product is
unlikely to be fed to cattle.
Although we recognized in our
rulemaking for boneless beef from Japan
that the product (inherently low-risk
boneless beef) is not intended for animal
consumption, we evaluated pathways
by which some small fraction of the
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product might inadvertently be fed to
cattle. We considered the possible
pathways to include restaurant
trimmings and plate waste, and the
direct feeding of human food waste to
cattle. We further evaluated pathways
by which home food waste and plate
waste can be fed directly to cattle, and
we did not identify any
epidemiologically significant pathways
for exposure of the U.S. cattle
population. Specifically for plate waste,
which is allowed to be incorporated into
ruminant feed, we considered that the
amount of meat in the plate waste
would be insignificant (Cohen et al.,
2001; 2003). Furthermore, because FDA
requires that the plate waste be further
heat processed for feed, it may be
subject to rendering processes that will
inactivate significant levels of the agent,
further reducing the level of infectivity
in the rendered product. (Cohen et al.,
2001; 2003).
The inherent (low risk) characteristic
of the product imported under the Japan
rule, coupled with the measures to
prevent contamination of the product
and the fact that the product is unlikely
to be fed to cattle, were the primary
factors in our evaluation. We did not
dismiss any risk based on quantity. We
considered the level of imports
specifically under that rule as an
additional limiting factor for any
infectious material, if present, in the
product.
Canadian cattle imported under this
final rule will be slaughtered for edible
meat production at slaughter plants
within the United States and would be
subject to FSIS’ slaughter restrictions.
These restrictions include ante-mortem
inspection and prohibition of the
slaughter of downer animals. In
addition, FSIS requires the removal of
SRMs, which is a critical risk measure
preventing contamination of edible meat
with BSE infectivity. We consider these
measures, combined with the fact the
edible meat is inherently low risk for
the BSE agent, to be sufficient to
mitigate the risk of exposing U.S. cattle
to the BSE agent, if present, via plate
waste.
Issue: One commenter noted that a
peer reviewer of the 2005 Harvard Risk
Assessment of Bovine Spongiform
Encephalopathy Update: Phase IA
suggested lowering the estimate that, at
ante-mortem inspection, a Federal
inspector will identify BSE symptoms in
infected animals 90 percent of the time.
The commenter stated further that the
Canadian BSE cases have not been
clinical suspects.
Response: The FSIS revision of the
ante-mortem assumptions demonstrates
that the assumed ante-mortem detection
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rate does not strongly influence the
results of the analysis. The commenter
noted that cutting the detection rates to
50 percent (ambulatory animals) and 25
percent (non-ambulatory animals)
increases the projected number of
infected animals by approximately 5
percent. Importantly from the
perspective of APHIS, this revision had
a limited impact on R0. The revised
FSIS assessment (dated December 26,
2006) included several changes relative
to the original FSIS assessment (dated
October 31, 2005).9 The mean value of
R0 increased from 0.24 in the original
FSIS assessment to a mean value of 0.27
in the revised FSIS assessment. The
95th percentile estimate for R0
increased from 0.45 in the original FSIS
analysis to 0.48 in the revised FSIS
analysis. In conclusion, the FSIS
analysis indicates that changing the
ante-mortem assumptions does not
appreciably alter the projected spread of
BSE. On the basis of the FSIS finding,
APHIS concludes that a change in the
ante-mortem detection rate of this
magnitude does not qualitatively alter
APHIS’ conclusions, and therefore does
not merit revision to the simulation
model.
Issue: One commenter cited published
literature described in the risk
assessment to point out the levels (in
grams) of highly infective brain tissue
that resulted in infection of calves
following experimental oral exposure.
The commenter then asked if, after
gauging what dosage is necessary to
transmit BSE orally, the risk to each
animal should be calculated based on
the number of times it has a feeding.
Response: There is no need to revise
the model in response to this comment
for the following reasons. First, the
model does not assume any threshold
below which exposure to BSE would
pose zero risk of infection. Second, and
as a result of the first point, the model
assumes that every exposure event
incrementally contributes to the risk of
infection.
Issue: One commenter noted that the
number of infected animals that survive
sufficiently long enough to develop
clinical disease is always small in the
exposure assessment (even under very
pessimistic assumptions), and that,
presumably, clinical animals will come
primarily from those animals
characterized as ‘‘beef repro’’ and
‘‘dairy’’ (APHIS 2006b, table 5). The
commenter questioned whether the
estimates of animals imported in these
classes of animals and their time9 The original and the revised FSIS assessments
may be viewed at https://www.fsis.usda.gov/Science/
Risk_Assessments/index.asp.
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dependent removal (death, slaughter,
and cull) rates from the population
before clinical signs develop were
realistic and validated.
Response: This comment appears to
consist of two parts. In the first, the
commenter asks if the estimates of
numbers of imported breeding animals
are realistic and valid, and in the
second, the commenter asks if the timedependent removal of these animals is
realistic and valid. Because different
sources of evidence support these two
components of the question, we address
them individually in the following
discussion.
As we explained in response to
another comment, our estimates of
imports of all cattle classes, including
breeding animals, were developed by
USDA, ERS. They are based on a wellaccepted, iterative method involving
expert opinion and country-commodity
specific modeling. Based on the above
description of this process, we expect
that alternative plausible assumptions
for the number of imported breeding
animals would not likely vary
substantially from those based on the
most current inputs.
With regard to the commenter’s
questions about time-dependent
removal of these animals (i.e., at what
point animals are removed from the
cattle population by, e.g., slaughter)
APHIS notes that imported animals are
integrated into the U.S. herd and thus
are removed (slaughtered) using the
same distribution used for native-born
U.S. cattle. The slaughter parameter
used in the Harvard model (Cohen et al.,
2003) ‘‘represents the probability that
cattle will be sent to slaughter. This
probability depends on the [animal’s]
type of production, age, and gender
(e.g., steers and heifers are sent to
slaughter earlier than dairy cows or
reproductive beef animals).’’ The
developers of the model based the
associated assumptions for the
parameter on the following sources,
listed in Cohen et al. 2003: USDA (U.S.
Department of Agriculture 1998a),
Radostits et al., 1994, and several
personal communications (Clay 2001;
Crandall 2001; Pinter 2001). The model
and its parameters have been subject to
previous peer review and have been
found to be realistic.
Issue: One commenter expressed
concern that, if an undetected BSEinfected cow were imported into a
family herd and, upon becoming
incapacitated, were sent to a local small
rural facility to be processed into beef
for the cow’s owners, BSE could enter
the food chain.
Response: The commenter seems to be
concerned about the possibility of BSE
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entering the human food chain after a
cow is slaughtered for personal use at a
custom slaughter facility. However,
such usage would be in contravention of
FSIS regulations. FSIS prohibitions on
the use of SRMs for human food apply
to cattle slaughtered for personal use at
custom facilities, as does FSIS’
prohibition of the use of all nonambulatory disabled cattle in the human
food chain (FSIS 2007).
Issue: A number of commenters
recommended that the provisions of the
proposed rule not be implemented
unless focused testing for BSE of cattle
imported from a BSE minimal-risk
region is carried out at slaughter. A
number of commenters recommended
that any bovine 30 months of age or
older imported into the United States
from a BSE minimal-risk region be
tested for BSE before being used for
food. Several commenters
recommended that USDA require testing
for BSE of all cattle imported to the
United States from countries in which
BSE has been diagnosed, such as
Canada. One commenter recommended
that the proposed rule not be
implemented until rapid-test technology
for BSE is provided to all U.S.
slaughtering facilities. Another
commenter recommended that USDA
allow slaughter establishments to
conduct additional tests to satisfy
consumer demands.
Response: Our peer-reviewed risk
assessment concluded that the
likelihood of BSE release from cattle
imported from Canada is likely to be
extremely low because (1) the
prevalence of BSE in Canada is
extremely low, and (2) measures
requiring imported animals to be born
on or after March 1, 1999, will further
decrease the likelihood that those
animals had been exposed to infectious
material. Moreover, the exposure
assessment for live animals qualitatively
indicates that because of the barriers to
BSE transmission in the United States,
the likelihood of BSE exposure and
establishment in the U.S. cattle
population as a consequence of
infectivity introduced via imports from
Canada is negligible.
Further, although we understand the
interest expressed by some commenters
in testing certain cattle for slaughter,
such comprehensive testing would not
necessarily yield accurate or useful
results. Current testing methodology can
detect a positive case of BSE only a few
months before the animal begins to
demonstrate clinical signs. The
incubation period for BSE—the time
between initial infection and the
manifestation of clinical signs—is
generally very long—on average about 5
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53339
years, which means that there is a long
period during which testing an infected
animal would produce negative but
incorrect results, especially if the
animal is clinically normal. The import
projections anticipate that the majority
of animals imported for immediate
slaughter and/or for feeding and
subsequent slaughter are young animals,
generally slaughtered at less than 30
months of age. Since current tests only
determine the presence of BSE shortly
before the likely onset of symptoms,
testing young, apparently normal
animals is not an effective use of the
tests. In addition, since SRM removal
requirements are in place, testing
apparently normal animals at slaughter
does not provide any significant
additional public health protective
measure. Heim and Kihm (2003) note
that it is questionable whether testing
all animals at slaughter provides any
measurable increase in consumer safety.
Additionally, they note that such testing
can be counter-productive since
measures such as SRM removal may not
be sufficiently emphasized due to the
perceived total reliability of the testing.
Given that testing of clinically normal,
apparently healthy cattle does not
provide meaningful data, combined
with the conclusions of the risk
assessment concerning the extremely
low likelihood of release and negligible
likelihood of exposure and
establishment in the U.S. cattle
population, testing these animals at
slaughter as commenters suggest is not
appropriate at this time.
Issue: A number of commenters stated
that APHIS should not expand the types
of bovines allowed importation from a
BSE minimal-risk region until it can be
shown that the current U.S. regulations
are being adequately enforced. Several
commenters cited as an example of
inadequate enforcement an incident
involving the importation and
movement to slaughter in the United
States of Canadian cattle over 30 months
of age. Of those commenters, some
expressed concern regarding the time it
took to trace the animals back.
Several commenters stated that
records from Washington State suggest
that Washington and several other
States are having difficulty tracking
hundreds of cattle that arrive from
Canada each week. Other commenters
stated that a number of cows entered the
United States from Canada without ear
tag identification or certificates of
health, or had eartag identification that
did not match the accompanying health
certificate.
Response: The commenters referenced
an alleged violation of the regulations in
which imported Canadian feeder cattle
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were reportedly sold through an auction
market in the United States. A detailed
investigation into the incident
demonstrated that the animals in
question were legally imported for
immediate slaughter.
Commenters also referenced issues
that State authorities identified in
tracking imported animals. Certain
States instituted policies or regulations
that required additional movement
controls and verification beyond the
APHIS import requirements. In these
instances, it is the responsibility of the
State authorities to monitor compliance
with their regulations and to follow up
on any reported violations. APHIS can
assist in resolving issues if requested.
APHIS port veterinarians inspect all
live animal shipments entering the
United States. These inspections
include careful review of the health
certificate accompanying the animals
and a visual inspection of the animals.
Live cattle presented at the port of entry
with no accompanying valid health
certificate are denied entry. We are not
aware of any instances where shipments
of cattle have entered through a
designated port of entry without a
health certificate. We recognize that
animals can lose eartags at various
points in the process and have
established procedures to reapply
eartags with appropriate documentation.
In addition, apparent transposition of
digits or similar errors in recording
eartag numbers can often be addressed
during consultation with CFIA and/or
the private veterinarian involved.
APHIS is not aware of significant or
repeated violations of the existing
APHIS import regulations, and no
evidence of such violations has been
provided by the commenters concerned.
Individual instances of errors or
violations can, and have, occurred.
These are investigated and dealt with
appropriately. At no time have any of
these errors presented a significant
threat to animal or public health.
Issue: One commenter stated that the
animal health risk assessment does not
address the risks to the U.S. cattle
industry, or to human health, of having
additional BSE cases discovered in the
United States.
Response: We disagree with the
commenter. In our risk assessment, we
addressed both the likelihood and the
consequences of the adverse event of
concern. We examined the likelihood of
BSE becoming established in the United
States, as well as the incremental
consequences that may occur for every
additional case that might be detected as
a result of implementing the proposed
rule. As discussed in the consequences
section of the risk assessment, based on
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the responses to cases discovered in the
United States since the initial finding of
BSE in Canada in 2003, we do not
expect additional costs (such as further
closure of export markets or reduction
in domestic consumption). When
combined with the expected number of
clinical cases, the resulting risk
estimation is negligible, as discussed in
the risk estimation section of the risk
assessment. Determining what portion
of the finding of negligible risk might be
borne by the U.S. cattle industry, as the
commenter requests, is unnecessary for
the purposes of our risk assessment.
Because we have determined the overall
risk to be negligible, we do not consider
it warranted to subdivide what is
already a negligible risk in assessing its
potential impact on various sectors.
The overall economic consequences
of the proposed rule on trade were
addressed by the Preliminary Regulatory
Impact Analysis that was conducted for
the proposed rule. That document
concluded that, although larger net
welfare benefits may be realized under
the scenario of no restriction by date of
birth on live bovine imports, the
proposed rule is preferable because it
would pose a lower risk of BSE
infectivity entering the United States via
imports of live bovines from Canada. In
response to public comments, the
revision of this analysis published with
the final rule has further examined the
welfare effects on certain sub-categories
of the cattle industry.
As noted, the risk assessment
specifically examines animal health, not
human health. However, there would be
no impact of detected cases on human
health, because such animals would be
removed from the human food supply.
The risk assessment did, however, note
the following and indicated that
additional discussion of the human
health aspects were included in the
environmental assessment. ‘‘Thus,
although human health is not the focus
of this assessment, we note that, even
our quantitative model, which includes
multiple sources of risk over-estimation,
indicates that, over the 20 years of the
analysis, only 45 cattle oral infectious
dose-50 (ID50) units will be available for
human exposure.’’ In comparison, as
discussed above, Comer and Huntly
(2003) estimated that 54 million bovine
oral ID50 units were available for human
consumption in Great Britain from 1980
to 2003. This extremely large amount of
available infectivity has resulted in 165
cases of vCJD identified in the United
Kingdom through April 2007, plus a few
additional cases identified in other
countries but attributed to exposure in
the United Kingdom. When compared to
the United Kingdom’s BSE experience
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and the associated estimate of available
bovine oral ID50 units, the expected, or
average value of 45 cattle oral ID50
would result in a miniscule amount of
the BSE infective agent that could
possibly be available for potential
human exposure in the United States
over a 20-year period (APHIS 2006). The
potential for human exposure under this
scenario is estimated at 1,200,000 times
less in the United States than what the
United Kingdom experienced during its
BSE epidemic. Whereas potential
human exposure to infectivity is
expected to be miniscule and
epidemiologically insignificant,
exposure (and hence potential human
health impacts) due to detected cases
would be nonexistent; detected cases of
BSE are removed from the food supply.
OIE Guidelines
The OIE is recognized by the World
Trade Organization (WTO) as the
international organization responsible
for development and periodic review of
standards, guidelines, and
recommendations with respect to
animal health and zoonoses (diseases
that are transmissible from animals to
humans). The OIE guidelines provide a
science-based reference document for
international trade in animals and
animal products. The OIE guidelines for
trade in terrestrial animals (mammals,
birds, and bees) are detailed in the
Terrestrial Animal Health Code (OIE,
2006a). The OIE guidelines on BSE are
contained in Chapter 2.3.13 of the
Terrestrial Animal Health Code and are
supplemented by Appendix 3.8.4 of the
Code.
Some commenters stated that our
proposed rule was inconsistent with
OIE guidelines. We discuss below those
areas addressed by the commenters.
Issue: Several commenters stated that
the proposed rule is inconsistent with
OIE guidelines because it did not
require’as the commenters stated OIE
guidelines recommend—that for
countries that do not have an effectively
enforced feed ban that is reducing the
incidence of BSE, the vertebrae and all
other SRMs be removed from cattle over
12 months of age.
Response: The OIE-recommended
guidelines regarding BSE contain
criteria for categorizing the risk of a
country as either negligible risk,
controlled risk, or undetermined risk.
The basis for categorization
encompasses several factors, including a
risk assessment, surveillance efforts,
regulatory structure for notifiable
diseases, and education and awareness
efforts. Canada has an effectively
enforced feed ban. Further, Canada has
been categorized by the OIE as
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controlled risk (OIE 2007b), rather than
as undetermined risk as implied by the
commenters. The OIE guidelines
recommend that certain SRMs be
removed from cattle over 30 months of
age for exports from countries that are
considered controlled risk, and cattle
over 12 months of age for exports from
countries that are considered
undetermined risk.
Issue: Several commenters stated that
the proposed rule did not comply with
OIE guidelines for either controlled risk
or undetermined risk countries
regarding the birth date of cattle in
relation to the date of effective
enforcement of a feed ban. The
commenters stated that the OIE
recommends that cattle not be exported
from a country of undetermined risk for
BSE, which the commenters stated
Canada qualifies as, unless the cattle
were born at least 2 years after the feed
ban was effectively enforced. Nor, said
the commenters, did the proposed rule
meet the OIE guidelines that cattle not
be exported from a controlled risk
country until after the date a feed ban
was effectively enforced.
Response: We disagree with the
commenters. As noted previously, the
OIE has categorized Canada as
controlled risk. Our proposed changes
are consistent with the OIE guidelines
for trade in live animals from a
controlled risk region. As part of the risk
analysis that APHIS conducted in
conjunction with its January 2005 final
rule that recognized Canada as a BSE
minimal-risk region, APHIS evaluated a
series of measures introduced in Canada
to prevent the feeding of ruminant
proteins to ruminant animals. USDA
considered the compliance activities
reported by CFIA as well as
epidemiological information in
concluding that compliance with the
feed ban was good, and that the feed ban
was effectively enforced.
The OIE guidelines do not define how
to determine the date the feed ban was
effectively enforced. APHIS identified
March 1, 1999, as the date of effective
enforcement of the feed ban in Canada
based on a careful evaluation of the full
panoply of features employed by the
feed ban and consideration of regulatory
enforcement actions (i.e., a practical
implementation period) and sufficient
additional time to allow previously
manufactured feed to cycle through the
system.
Issue: Several commenters stated that
APHIS published the proposed rule
despite the fact that Canada does not
meet OIE guidelines for testing for BSE,
and requested that APHIS withdraw or
delay this rulemaking until Canada
significantly increases its BSE testing.
One commenter stated that, to meet OIE
testing guidelines, Canada needs to test
with negative results 187,000
consecutively targeted cattle with a BSE
risk equal to that in the casualty
slaughter age between 4 and 7 years, in
order to be confident that the BSE
prevalence in Canada is not more than
1 in 100,000. However, said the
53341
commenter, Canada tested only 143,528
total cattle in the period from 2004
through February 12, 2007, with 8
positive cases found during that period.
Response: We disagree with the
conclusions and assertions of the
commenters. The OIE Terrestrial
Animal Health Code, 2006, Appendix
3.8.4, contains guidelines for BSE
surveillance. These guidelines describe
a weighted points system for BSE
surveillance samples and suggest total
points targets for what is considered as
either Type A or Type B surveillance.
As noted in the Code, ‘‘The application
of Type A surveillance will allow the
detection of BSE around a design
prevalence of at least one case per
100,000 in the adult cattle population in
the country, zone or compartment of
concern, at a confidence level of 95
percent.’’ Based on this definition, we
assume the comments described above
refer to Type A surveillance. The points
target for Type A surveillance in a
country such as Canada with an adult
cattle population of more than 1,000,000
is 300,000 points, to be obtained over a
7-year period.
Under the OIE guidelines, specific
‘‘point values’’ are assigned to each
sample, based on the surveillance
stream or subpopulation of animals
from which it was collected, as well as
the likelihood of detecting infected
cattle in that subpopulation. Table 4,
below, outlines the point values for
samples obtained from the different
surveillance streams:
SURVEILLANCE POINT VALUES FOR SAMPLES COLLECTED FROM ANIMALS IN THE GIVEN SUBPOPULATION AND AGE
CATEGORY
Surveillance subpopulation
Routine slaughter
Fallen stock
Casualty slaughter
Clinical suspect
Age >1 year and <2 years
0.01
0.2
0.4
N/A
Age >2 years and <4 years (young adult)
0.1
0.2
0.4
260
Age >4 years and <7 years (middle adult)
0.2
0.9
1.6
750
Age >7 years and <9 years (older adult)
0.1
0.4
0.7
220
0.2
45
Age >9 years (aged)
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0.0
0.1
As demonstrated in table 4, a sample
from the specific surveillance
subpopulation where BSE is most likely
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to be detected—i.e., a middle adult
clinical suspect—provides the most
surveillance points. Conversely, a
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sample from the subpopulation where
BSE is least likely to be detected—
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generally routine slaughter—provides
the least points.
It appears that the commenter
calculated the number of samples
necessary from an assumed surveillance
subpopulation. That is, if a country
samples only middle adult casualty
slaughter animals at 1.6 points per
sample, it would need to sample
187,000 cattle in this specific
subpopulation to obtain 300,000 points.
However, it is inaccurate to compare
such a calculation to Canada’s
surveillance efforts. The commenter
referred to surveillance conducted in
Canada from 2004 through February
2007—a period of slightly more than 3
years. However, as noted, the OIE
guidelines provide for points targets to
be met over a 7-year period. Therefore,
a valid comparison of the OIE
guidelines and the testing conducted in
Canada would need to be based on
surveillance totals from, e.g., January
2000 through December 2006.
More significantly, the commenter
appeared to assume that Canada is
sampling only one specific surveillance
stream—casualty slaughter animals from
4 to 7 years of age. Attachment 1 of the
risk assessment conducted for this
rulemaking—‘‘Estimation of BSE
Prevalence in Canada (APHIS 2006c)’’—
contains tables that allocate Canadian
surveillance samples into the different
surveillance streams. In every year from
1999 through August 2006, animals
from three different surveillance
streams—fallen stock, casualty
slaughter, and clinical suspect—of all
ages were sampled. Therefore, the
points value for each sample will vary
in line with the previously provided
table. A summary of OIE points can be
calculated from the information
provided. For example, data from
surveillance conducted in Canada in
2005 for only one surveillance stream—
clinical suspect—show that, in that
year, 2 clinical suspects less than 2
years old were sampled (0 points), 43
clinical suspects 2 to 3 years of age were
sampled (11,180 points), 120 clinical
suspects 4 to 6 years of age were
sampled (90,000 points), 68 clinical
suspects 7 to 8 years of age were
sampled (14,960 points), and 194
clinical suspects greater than 9 years of
age were sampled (8,730 points).
Testing of the 194 clinical suspects
sampled in 2005 provided a total of
124,870 points for this 1 surveillance
stream in 1 year. The total number of
OIE points accumulated by Canadian
surveillance over the 7-year period
ending at August 2006 is 922,176. This
far exceeds the OIE point target of
300,000 points for Type A surveillance.
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Issue: Several commenters stated that
the proposed rule did not comply with
the OIE guidelines with regard to the
importation of SRMs. The commenters
stated that the OIE recommends that
SRMs not be imported for feed or
fertilizer and the proposed rule would
allow SRMs to be used for non-ruminant
feed and fertilizer.
Response: The commenters are correct
that the OIE guidelines recommend that
certain tissues—SRMs—should not be
traded. Specifically, the guidelines
recommend that SRMs ‘‘should not be
traded for the preparation of food, feed,
fertilizers, cosmetics, pharmaceuticals
including biologicals, or medical
devices.’’ It also states that ‘‘protein
products, food, feed, fertilizers,
cosmetics, pharmaceuticals or medical
devices prepared using these
commodities (unless covered by other
Articles in this Chapter) should also not
be traded.’’ However, the Code also
includes guidelines for trade in live
cattle—from which such materials could
be derived after export to the recipient
country—from countries of any risk
status, thus creating an apparent
contradiction in recommendations.
We recognized in our risk assessment
that SRMs from live cattle imported
under these conditions could enter the
U.S. system, similar to SRMs from U.S.
cattle. The assessment acknowledges
that SRMs from imported animals—just
as those from domestic animals—can
enter the rendering system in the United
States, and the quantitative exposure
model in the risk assessment
specifically simulates this situation.
Certain rendered protein products—
bone meal, for example—can be
included in fertilizer. However, this is
not a common practice in the United
States, as the vast majority of rendered
protein products are sold for use in
animal feed. Raw or untreated tissues
are not generally used as fertilizer, and
in fact are often prohibited from being
spread on land. Therefore, any
consideration of risk from fertilizer
would be an evaluation of the risk of
cattle exposure to oral consumption of
fertilizer that contains in part rendered
protein.
Our quantitative exposure model
evaluates the potential oral exposure of
cattle to feed containing infected
rendered protein products. It does not
specifically model potential exposure
through fertilizer. However, it assumes
that all rendered ruminant protein
products are sold for feed use.
Therefore, any of the infectivity
contained in rendered ruminant protein
is simulated through the potential for
direct feed exposure—either through
misfeeding, cross-contamination, or
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poultry litter. Feed constitutes a more
significant pathway than potential
consumption of a component of a
fertilizer product after it is spread on a
pasture. Therefore, any potential
exposure through fertilizer would be
assumed to be far less than exposure
through feed, which is modeled in the
risk assessment.
For the reasons discussed above, we
disagree that this rule is inconsistent
with OIE guidelines. In those cases
where one might see in the OIE
guidelines an internal contradiction,
that contradiction is much more
apparent then real, and we consider this
rule to be consistent with the intent and
objectives of the guidelines. Therefore,
we are making no changes based on the
comments.
International BSE Classification of
Canada and the United States
Issue: At the time APHIS was
accepting public comments on its
January 2007 proposed rule, the OIE
was in the process of completing its
evaluation of countries internationally
to determine which BSE risk category
would be appropriate to each country
evaluated. Several commenters
recommended that our proposed rule be
delayed until the OIE released its
determinations. Commenters stated that
waiting for release of the OIE
designations would allow the U.S.
categorization of BSE minimal-risk
regions to be made consistent with OIE
guidelines. Additionally, stated some
commenters, the proposed rule could
negatively influence the OIE’s BSE risk
categorization of the United States. One
commenter recommended that the
rulemaking be postponed until the
European Food Safety Authority (EFSA)
announced its BSE risk categorization of
various countries, including Canada.
Response: Under the OIE risk
classification system, a country can be
considered to be ‘‘negligible risk,’’
‘‘controlled risk,’’ or ‘‘undetermined
risk’’ with regard to BSE. Based on the
risk classification of a country, the OIE
provides guidelines for the safe trade of
cattle and cattle products. As noted
above, at the May 2007 annual General
Session of the OIE International
Committee, a list of countries
recognized as being BSE controlled risk
or negligible risk was confirmed. Both
the United States and Canada were
confirmed as BSE controlled risk
countries (OIE 2007b).
Request To Allow Imports From the
European Union
Issue: One commenter requested that
APHIS implement OIE import
guidelines regarding BSE or,
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alternatively, recognize the European
Union as a BSE minimal-risk region.
Response: As noted above, it is
APHIS’ intent to develop rulemaking
that would incorporate OIE guidelines.
Commodities Eligible for Importation
Under This Rule
We proposed to allow the
importation, under certain conditions,
of live bovines for any use born on or
after a date determined by APHIS to be
the date of effective enforcement of a
ruminant-to-ruminant feed ban in the
region of export; blood and blood
products derived from bovines; and
casings and part of the small intestine
derived from bovines.
Although commenters addressed the
provisions of our proposed rule
regarding each of these commodities,
the great majority of commenters
focused on the potential importation of
live bovines. We discuss below first the
issues raised concerning live bovines,
then the commenter issues regarding
bovine blood and blood products and
then those regarding the small intestine,
including casings derived from the
small intestine.
Those commenters who addressed the
importation of live bovines discussed
which bovines should be eligible for
importation with regard to usage and
date of birth, identification of the
animals, verification that the animals
are imported in compliance with the
regulations, sealing of means of
conveyance carrying the animals, and
monitoring of imported cattle once in
the United States.
Live Bovines
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Date of Birth Eligibility
Issue: A number of commenters
questioned how it will be determined
whether a bovine intended for
importation from Canada was born on or
after March 1, 1999. The commenters
stated that it will not be feasible to use
dentition to determine the age of
imported bovines, particularly in
animals over 4 years of age. In many
cases, said the commenters, Canadian
veterinarians would have to accept
producers’ statements as the only source
of verification of the age of the cattle.
The commenters stated that the
Canadian national cattle identification
program was not made mandatory until
2002, and that it is still not mandatory
in Canada to enter the entire birth date
information into the database. Several
commenters stated that it is nearly
impossible to verify the actual age of
older Canadian cattle, because the
Canadian animal identification
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requirement applies only to cattle that
leave the farm.
Response: The provisions in
§ 93.436(a)(3) and (b)(4) of this rule
provide that bovines are not eligible for
importation from a BSE minimal-risk
region unless they are accompanied by
certification that, among other things,
the animals were born on or after March
1, 1999. As provided in § 93.405(a),
such certification must be issued by a
full-time salaried veterinary officer of
the national government of the region of
origin, or by a veterinarian designated
by the national government of the region
of origin and endorsed by a full-time
salaried veterinary officer of the
national government of the region of
origin, representing that the veterinarian
issuing the certificate was authorized to
do so. It is incumbent upon the
individual issuing or endorsing the
certificate to ascertain whether an
animal’s date of birth can be determined
with the accuracy necessary for such
certification. As the commenters imply,
dentition can be used to adequately
determine the birth date of animals
below about 4 years of age. Specifically,
if an animal does not have all of its
permanent teeth erupted, it is less than
4–5 years of age and therefore was born
after March 1, 1999. However, if all
permanent teeth are present and in
wear, dentition does not provide an
estimate of birth date specific enough to
support certification that the animal was
born on or after March 1, 1999.
We recognize that Canada’s
mandatory identification requirements
did not take effect until 2002, and also
that these requirements do not mandate
that birth date information be entered
into the database. However, we also
note that provisions have been
established for birth date information to
be entered at any time, with appropriate
documentation available to support
such information. The number of these
age-verification entries continues to
increase, with over 3.5 million birth
dates submitted to the Canadian Cattle
Identification Agency (CCIA) database
by late 2006 (CCIA, 2006). We recognize
that it is likely that owners of some
bovines may not be able to provide the
documentation regarding an animal’s
birth date that is necessary for the
required certification. In those cases,
even if an animal was born on or after
March 1, 1999, the animal would not be
eligible for importation into the United
States.
Permanent Identification of Country of
Origin
Issue: Under the provisions of the
proposed rule, cattle imported from
Canada for other than immediate
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53343
slaughter would have to be permanently
and humanely identified before arrival
at the port of entry with a distinct and
legible mark identifying the exporting
country. As proposed, acceptable means
of permanent identification would
include a mark applied with a freeze
brand, hot iron, or other method; a
tattoo applied to the inside of one ear
of the animal, or other means of
permanent identification if deemed
adequate by the Administrator. For
bovines imported from Canada, a brand
would have to read ‘‘CLN’’ and a tattoo
would have to read ‘‘CAN.’’
A number of commenters addressed
the issue of permanent identification of
bovines as to the country of export.
Several commenters recommended that
the regulations require that such
identification be applied with a hot-iron
brand, and that a ‘‘hair brand’’ not be
considered acceptable means of
identification.
Response: A hair brand would not
meet the requirements of the
regulations, in that it could not be
depended upon to provide permanent
identification of the animal’s country of
export. However, we do not consider it
necessary to list in the regulations all
the forms of identification that would
not be considered adequate to meet the
intent of the regulations.
Issue: Several commenters addressed
the requirement for permanent
identification of the country of export as
it would apply to bison. The
commenters stated that a brand on the
right hip or an ear tattoo are not the
preferred alternatives, because of
unnecessary stress on the animals and
handlers. The commenters stated that a
more humane means of bison
identification, such as electronic tags
(dual tags if necessary), could readily
meet the need of tracking the origin of
the bison and the movement patterns in
Canada and the United States.
Response: The type of identification
recommended by the commenters
would provide the individual unique
identification required by the
regulations to facilitate traceback of the
animal. Although the current
regulations in § 93.436 require that such
identification be provided by an official
eartag of the country of origin, in August
2006 we have proposed to allow for
forms of individual identification other
than eartags.10
10 We proposed (71 FR 45439–45444, Docket No.
APHIS–2006–0026) to allow the individual
identification to be provided with some form of
identification other than an eartag. We solicited
comments concerning our proposal for 60 days
ending October 10, 2006. On November 9, 2006, we
published a document in the Federal Register (71
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However, we consider it necessary
that the animal also be marked in some
permanent and easily visible way as
having been imported from a BSE
minimal-risk region. In the case of bison
from Canada, this would be a brand or
other permanent ‘‘CLN’’ mark on the
right hip, an ear tattoo with the letters
CAN, or some other means of permanent
identification if deemed adequate by the
Administrator to humanely identify the
animal in a distinct and legible way as
having been imported from the BSE
minimal-risk exporting region. The type
of identification recommended by the
commenters would not allow for easily
visible identification of the country of
origin.
Issue: A number of commenters
disagreed that an ear tattoo would be an
effective permanent means of
identifying the country of origin of a
bovine. The commenters stated that
tattoos applied inside an animal’s ear
frequently become illegible after a
period of time, and further, that tattoos
may not be visible without catching the
animal and examining it in a chute or
other restraint system. The commenters
recommended that, if tattoos are
allowed, the regulations require that
animals so identified be restrained and
examined in the country of export to
confirm that the tattoo is legible and
permanent, and that such confirmation
be indicated on signed documentation
accompanying the animals to the United
States.
Response: As discussed in our
proposed rule, we agree that tattoos
might not be the most readily visible
means of identification of live animals
in groups of animals. However, the
purpose of requiring permanent
identification of the animal’s country of
export is to expedite initial
identification of an animal’s country of
export in the event the animal is
diagnosed with BSE. Such a diagnosis
cannot be confirmed on a live animal.
Once the animal has been euthanized or
has otherwise died, an ear tattoo will be
an effective means of identification.
Issue: Several commenters stated that
the APHIS Administrator should be
required, upon request, to evaluate
alternative means of permanent
identification and, if they are
functionally equivalent to the existing
methods, be required to approve them.
Response: Paragraph (b)(2)(iii) of
§ 93.436 (of this rule provides for such
approval by the Administrator of
FR 65758–65759, Docket No. APHIS–2006–0026)
reopening and extended the comment period until
November 24, 2006. We received a total of 10
comments by that date. We are considering the
issues raised by the commenters and will address
them in a separate rulemaking document.
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alternative means of permanent
identification.
Issue: Several commenters
recommended that a hot-iron brand on
the right hip be required on all cattle
crossing the U.S. border.
Response: As noted above, we
proposed to require a permanent mark
identifying the animal’s country of
origin only for cattle imported from a
BSE minimal-risk region for other than
immediate slaughter. We do not
consider it necessary for cattle imported
from a BSE minimal-risk region for
immediate slaughter to be permanently
identified as to country of export. Such
animals will be moved to the
slaughtering establishment in a group
and the movement documentation
accompanying such animals will be
sufficient to provide ready identification
of the animals’ country of origin.
Issue: One commenter recommended
that the regulations require that each
animal entering the United States have
permanent identification by which the
animal could be traced back to its farm
of origin.
Response: The commenter’s
recommendation refers to two types of
identification that are already addressed
by this rule. In this rule, paragraphs
(a)(2) and (b)(3) of § 93.436 already
require each bovine imported into the
United States from a BSE minimal-risk
region to be officially identified with an
official eartag that provides unique
individual identification that is
traceable to the premises of origin of the
animal. (As noted above, we have
proposed to allow for forms of
individual identification other than
eartags). This rule requires, further, that
no person may alter, deface, remove, or
otherwise tamper with the official
identification while the animal is in the
United States or moving into or through
the United States, except that the
identification may be removed at the
time of slaughter.
In addition to the individual
identification that allows for traceback
to the animal’s premises of origin, the
regulations also require that all cattle
imported from a BSE minimal-risk
region be permanently identified as to
country of origin as described above. As
discussed above, we do not consider it
necessary for bovines imported for
immediate slaughter to have this
additional permanent identification as
to country of origin.
Issue: One commenter requested that
APHIS provide details of its protocol
and criteria for ensuring that all live
cattle imported from Canada have
permanent identification maintainable
until harvest.
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Response: In § 93.436(b) of this rule,
we give examples of means of
permanent identification that would be
considered acceptable. Acceptable types
of permanent identification include a
mark applied with a freeze brand, hot
iron, or other method, or a tattoo
applied to the inside of one ear of the
animal. Any other types of permanent
identification approved by the
Administrator would have to be as
effective as the examples cited in
providing a permanent, distinct, and
legible mark.
Individual Identification of Bovines
Issue: One commenter recommended
that all cattle imported from Canada that
are not moved directly to slaughter be
required to be identified by a low
frequency ISO compliant radio
frequency tag placed in the left ear.
Response: As noted above, we have
proposed to provide for forms of
individual identification other than
eartags, provided the identification can
be used to trace the animal back to its
premises of origin. We do not consider
it necessary to mandate the use of any
particular technology for meeting that
criterion.
Issue: One commenter recommended
that the regulations require that animals
intended for importation into the United
States from a country with a verified
case of BSE be enrolled in a third-party
source and age identification program
that uses individual electronic
identification devices.
Response: With regard to bovines
intended for importation into the United
States from a BSE minimal-risk region,
the regulations already require that such
animals be individually identified with
unique identification that enables
traceback to the premises of origin of the
animal. Additionally, under this rule,
bovines imported from Canada must be
accompanied by certification issued or
endorsed by the Canadian Government
that the animals were born on or after
March 1, 1999. After having evaluated
the veterinary infrastructure of countries
wishing to import animals and animal
products into the United States, APHIS
accepts official certification from those
countries that commodities intended for
export to the United States are in
compliance with U.S. import
regulations, just as U.S. trading partners
rely on official U.S. certification that
products exported from the United
States meet the recipient country’s
requirements.
Sealing of Means of Conveyance
Issue: The regulations for importing
live bovines from BSE minimal-risk
regions have required that the bovines
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be imported in a means of conveyance
sealed in the region of origin with seals
of the national government of the region
of origin. In our proposed rule, we
proposed to remove the requirement
that bovines imported into the United
States from BSE minimal-risk regions
for other than immediate slaughter enter
the country in sealed conveyances. We
additionally proposed to remove the
requirement that means of conveyance
carrying bovines into the United States
from minimal-risk regions for
immediate slaughter be sealed in the
region of export and to require instead
that means of conveyance carrying
bovines into the United States from
Canada be sealed at the U.S. port of
entry with seals of the U.S. Government.
Several commenters specifically
supported the proposed change to
require sealing of means of conveyance
at the port of entry, rather than in the
country of export.
One commenter stated that the
proposed change to require sealing at
the port of entry would allow APHIS
less oversight of shipments and less
opportunity to ensure that each animal
in the shipment is accurately identified
and of the appropriate age.
Several commenters recommended
that APHIS specify which country or
agency will be responsible for sealing a
means of conveyance at the port of
entry.
Response: We disagree that requiring
sealing of means of conveyance at the
port of entry will allow APHIS less
oversight of shipments or cause
decreased ability to ensure that the
animals are being shipped in
compliance with the regulations. The
primary verification that the animals
meet the requirements of the regulations
will remain as it has been—i.e.,
certification by the country of export
that the requirements of the regulations
have been met.
However, we believe it is necessary to
continue to require sealing of means of
conveyance transporting bovines from
Canada to immediate slaughter as a
mitigative measure against diseases
other than BSE. Cattle imported from
Canada for immediate slaughter are not
subject to tuberculosis and brucellosis
testing requirements that would
otherwise be applied to animals
imported into the United States.
Therefore, we would continue to require
that such cattle be moved directly to
slaughter in a sealed means of
conveyance. (APHIS had been requiring
such sealing at the port of entry even
before our November 2003 proposal
regarding BSE. However, the
requirement for sealing was being done
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as APHIS policy, and was not specified
in the regulations.)
As the commenters noted, this rule
will remove the requirement that the
sealing of the means of conveyance be
done in the region of export. That
requirement was included in the
January 2005 final rule in response to
comments from members of the public
who expressed concern that requiring
sealing at the port of entry could be
harmful to the welfare and quality of the
animals, due to delays at the port of
entry. Under the provisions of this
proposed rule, however, we do not
expect undue delays of shipments at the
port of entry. When a means of
conveyance carrying bovines for
immediate slaughter arrives at the U.S.
port of entry, APHIS inspectors would
confirm that the animals are as
described on the certificate that must
accompany the animals being imported,
but generally would not require that the
animals be offloaded from the means of
conveyance. Therefore, requiring that
the sealing of the means of conveyance
take place at the port of entry would not
cause measurable delay of the shipment.
Further, sealing at the port of entry
rather than in the region of export will
reduce the time the animals will need
to be contained in a sealed means of
conveyance and reduce the likelihood
that a seal will need to be broken
between the time it is applied and the
arrival of the animals at a slaughtering
establishment.
We do not consider it necessary to
specify which agency will seal means of
conveyance at the port of entry with
seals of the U.S. Government. In each
case, the means of conveyance will be
sealed by an APHIS employee.
Movement of Cattle for Other Than
Immediate Slaughter
Issue: Some commenters who
opposed allowing the importation from
Canada of bovines 30 months of age or
older urged the continuation of the
current restrictions on movement in the
United States of cattle moved to a
feedlot, as well as continuation of the
current requirements regarding sealing
of conveyances carrying such animals
and the requirement that the animals be
accompanied by an APHIS-issued
movement permit.
Response: The sealing and movement
restrictions referred to by the
commenters were included in our
January 2005 final rule to ensure that
live bovines from BSE minimal-risk
regions were imported and slaughtered
before the age of 30 months. At the time
we published that final rule, we had not
formally assessed the disease risk of
allowing the importation of live bovines
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53345
30 months of age or older from BSE
minimal-risk regions. Since that time,
we have conducted an assessment of the
risk of such importations, which we
discussed in our January 2007 proposed
rule and made available with that
proposed rule. Our risk assessment
indicates that there is a negligible
likelihood of U.S. cattle being exposed
to BSE and of BSE becoming established
in the U.S. cattle population as a
consequence of this rule.
Under this final rule, bovines from a
BSE minimal-risk region will not have
to be imported and slaughtered before
they are 30 months of age. Therefore, it
is not necessary to retain provisions in
the regulations that were designed to
help ensure that bovines imported from
a BSE minimal-risk region are moved
directly to a feedlot and then to
slaughter as an easily identifiable group.
Request To Exempt Cattle for Immediate
Slaughter From Birth Date Requirement
We proposed to require that live
bovines imported from BSE minimalrisk regions have been born on or after
the date recognized by APHIS as the
date of effective implementation of a
ruminant-to-ruminant feed ban in the
region of export. We proposed to apply
this requirement to all bovines imported
from a BSE minimal-risk region,
whether they are imported for
immediate slaughter or for some other
usage.
Issue: A number of commenters stated
that the eligibility of cattle to be
imported for immediate slaughter
should not be dependent on when the
animals were born. The commenters
stated that such animals do not present
a BSE risk justifying such a condition,
and that APHIS has not demonstrated
such a risk. Several commenters stated
that the risk assessment APHIS
conducted for the proposed rule is
based on the premise that slaughter
cattle will be eligible for importation
from Canada no matter what their date
of birth.
Additionally, commenters argued that
requiring cattle moving directly to
slaughter to have been born on or after
March 1, 1999, would be inconsistent
with the January 2005 final rule, which
provided for the importation of beef
derived from cattle of any age if
requirements for the removal of SRMs
are met. The commenters stated that
allowing the importation of beef from
cattle of any age while prohibiting the
importation of cattle born before March
1, 1999, suggests that SRM removal can
be accomplished more effectively in a
foreign country than in the United
States.
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Commenters stated further that
scientific evidence overwhelmingly
demonstrates that the safety of food
products derived from cattle is not
dependent on the age of the animal, but
on whether SRMs have been removed
and disposed of. The commenters stated
that complete control of cattle imported
from BSE minimal-risk regions can be
assured by requiring movement under
Government seal, as we proposed. As an
additional safeguard, stated the
commenters, USDA regulations require
that if an animal showing clinical signs
of BSE risk is tested for the disease at
slaughter, the carcass and parts derived
from the animal cannot enter the food
supply unless the animal tests negative
for BSE.
Response: The commenters who
recommended allowing the importation
of cattle of any age from BSE minimalrisk regions, regardless of date of birth,
raised several distinct issues in support
of their recommendations. We agree
with the commenters who stated that
the removal and disposal of SRMs is the
key factor in the food safety of products
from bovines used for human
consumption. However, the risk
assessment conducted for the proposed
rule specifically addressed the risk to
animal health. The risk of transmission
to U.S. cattle occurs when infectious
tissues—most likely SRMs—
inadvertently and/or in contradiction to
U.S. feed regulations are rendered and
included in ruminant feed and fed back
to cattle. The risk of BSE-infected SRMs
being present in the United States,
while minimal, might be increased to
some extent if cattle from BSE minimalrisk regions were allowed to be
imported for immediate slaughter
regardless of date of birth. The
commenters are incorrect that our risk
assessment did not take into account the
date of birth of slaughter cattle. As
described in the risk assessment, the
requirement that animals for import be
born after a certain date is one
mitigation step that helps reduce the
risk that infected animals will be
imported, and therefore helps reduce
the possibility that their SRMs will be
incorporated into the ruminant feed
chain in the United States.
Request for Restrictions on Use of
Imported Cattle
Issue: As discussed above, we
proposed to allow the importation of
bovines from BSE minimal-risk regions
for any use, provided the animals were
born on or after the date recognized by
APHIS as the date of effective
implementation of a ruminant-toruminant feed ban in the region of
export. This provision allows bovines to
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be imported for immediate slaughter or
for some other usage, such as breeding
or feeding and then slaughter. It differs
from the regulations, that have been in
place, which have limited the
importation of bovines from BSE
minimal-risk regions according to both
the age of the animal and the intended
usage of the animal in the United States
(only those animals moved to
immediate slaughter, or to one feedlot
and then directly to slaughter, have
been eligible for importation).
A number of commenters opposed the
proposed removal of restrictions on how
cattle imported from BSE minimal-risk
regions may be used. Although most of
these commenters did not object to the
importation of cattle born on or after the
date of effective implementation of a
feed ban if the cattle were moved in a
sealed means of conveyance directly to
immediate slaughter, or to a single
feedlot and then to slaughter, they
expressed concern regarding the
potential importation of cattle intended
for breeding or as replacement animals
in dairy herds.
Some of the commenters stated that
BSE-infected cattle imported from BSE
minimal-risk regions for breeding or
herd replacement may not show clinical
symptoms of BSE infection for many
years, allowing BSE to incubate in U.S.
cattle herds, and that an outbreak of BSE
in the United States due to such
imported cattle would be devastating to
the U.S. dairy industry.
A commenter stated that, at the 95th
percentile confidence for model
simulations of Canadian BSE prevalence
in the APHIS risk assessment, 180 new
BSE cases occur over 20 years, and that
90 percent of these new cases would be
expected to be in animals already
infected with BSE when imported from
Canada. Therefore, stated the
commenter, almost all new cases of BSE
expected in the United States will be
from BSE-infected cattle imported from
Canada and that any U.S.-born cases
will be the result of importing breeding
animals. Commenters stated further
that, according to USDA, younger cattle
are more susceptible to BSE and require
less BSE-contaminated feed to become
infected, and that since it is likely that
younger cattle will be the ones imported
for breeding or replacement purposes,
the chance of introducing BSE into the
United States from Canada is magnified.
Commenters stated that, although a
series of risk mitigations are in place,
these are different when it comes to
animals imported for breeding versus
those going directly to slaughter.
Response: The risk of BSE
transmission to U.S. cattle occurs when
infectious tissues—most likely SRMs—
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inadvertently and/or in contravention of
U.S. feed regulations are rendered and
included in ruminant feed and fed back
to cattle. This risk is the same whether
the animals were imported for
immediate slaughter or were imported
for breeding and are slaughtered later,
and the series of risk mitigations or
steps that prevent the transmission of
BSE are the same, regardless of the
purpose of the imported animal. While
it is true that the level of infectivity in
a BSE-infected bovine has been shown
to increase as an animal ages, the
amount of infectivity in, for example, a
7-year-old cow infected at 1 year of age
would be the same at slaughter whether
it was imported as a 1-year-old infected
cow and used for breeding in the United
States until it was 7 years old, or
whether it was imported as a 7-year-old
cull cow for immediate slaughter.
The U.S. feed ban prohibits the use of
most mammalian protein in ruminant
feed. The mammalian protein
referenced could be derived from
slaughterhouse offal—including SRMs—
from animals imported for immediate
slaughter, or from slaughterhouse offal
derived from animals imported for
breeding that have reached the end of
their useful life in the United States.
The protein could also be derived from
the carcass of an animal imported for
breeding that died other than by
slaughter. The feed restrictions on the
use of rendered protein derived from
any of those scenarios would be exactly
the same.
The commenters are correct that BSEinfected cattle may not show clinical
signs for many years, due to the long
incubation period for this disease as
explained in the risk assessment.
However, as long as the animals were
born on or after March 1, 1999, the
likelihood of any individual animal
having been exposed to and infected
with BSE, and subsequently releasing
BSE infectivity into the United States, is
negligible. There is no expected
difference in the likelihood of BSE
infection in two animals born on or after
March 1, 1999, and raised in Canada,
one imported into the United States as
a young animal for breeding purposes
and slaughtered at the end of its
productive period, and one used as a
breeding animal in Canada, and
exported for immediate slaughter in the
United States at the end of its
productive period. Furthermore, BSE is
not a contagious disease and does not
spread by casual animal contact.
Therefore, while an individual animal
in a herd may be infected, that does not
mean that other animals in that herd are
at risk of becoming infected via spread
from that animal.
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Regarding the commenter’s reference
to our model simulation, we believe the
commenter did not correctly interpret
the results from the simulation. For
sensitivity analysis 5 (pessimistic value
for assumed BSE prevalence in Canada),
the 95th percentile value for total
infected cattle in the United States over
a 20-year period amounts to 180
animals. The 95th percentile value for
endogenous BSE-infected cattle over
that period is 75, suggesting that
180¥75 = 105 BSE cases are imported
over that period, not 160 animals, as
suggested by the commenter.11
Also, although our quantitative
exposure models project that new cases
of BSE in the United States would be
transmissions secondary to the
importation of infected cattle from
Canada, we note that the United States
has identified two indigenous cases of
BSE. Given this fact, one cannot
categorically state that any such cases
identified ‘‘will be from BSE-infected
cattle directly imported from Canada.’’
We explained in the risk assessment
that there is an apparent agesusceptibility in regard to BSE,
specifically noting that susceptibility in
cattle declines with age. However, we
disagree with the commenter’s
conclusion that, based on this fact,
importing younger animals—
specifically breeding animals as they are
generally imported at less than 2 years
of age—presents a magnified risk.
Susceptibility is not the same as
likelihood of being infected. As an
example, the commenter’s conclusion
means that any animal born within the
past 2 years would have a higher
likelihood of being infected than an
animal born 6 years ago. Given equal
exposure a younger animal may be more
susceptible to infection. However, as
noted in the risk assessment, the overall
prevalence in Canada is extremely low
and BSE controls such as the feed ban
are effectively enforced, so the chance
that a given animal of any age had been
exposed to an adequate amount of
11 Note that this estimate for the 95th percentile
for imported cases (105) is approximate. The 95th
percentile values for the total number of infected
animals (180) and the number of endogenous cases
(75) are estimated independently. In particular, all
of the trials are first ranked according to the total
number of endogenous cases, allowing
identification of the 95th percentile value. The
same is then done in order to identify the 95th
percentile value for the total number of BSE cases.
As a result, the 95th percentile values may be
selected from different simulation trials. Because
the number of endogenous cases influences the
number of total cases, these two quantities are
(imperfectly) correlated, however. That is,
simulation trials that project a large number of
endogenous cases also project a large total number
of BSE cases. Hence, the actual 95th percentile
value for the total number of imported BSE cases
is likely to be similar to 105.
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infectivity at a susceptible age i.e., the
likelihood of being infected) is
extremely small.
Monitoring of Imported Cattle
Issue: A number of commenters
expressed concern that the proposed
rule did not explicitly provide for a
system to monitor the movement in the
United States of cattle imported from
BSE minimal-risk regions, specifically
Canada. Some commenters limited their
discussion to cattle 30 months of age or
older. Commenters recommended that
the regulations include an accounting
procedure capable of monitoring the
movement of imported animals from
entry into the United States until
slaughter, including changes in
ownership of the animals.
Response: The regulations currently
include movement conditions for
bovines from BSE minimal-risk regions
imported for other than immediate
slaughter. Such bovines must be
imported in a sealed conveyance and be
moved directly from the port of entry to
a feedlot identified on APHIS Form VS
17–130 or other movement
documentation required by the
regulations. The APHIS Form VS 17–
130 or other movement documentation
must identify the physical location of
the feedlot, the individual responsible
for the movement of the animals, and
the individual identification of each
animal. The bovines must remain at the
feedlot until transported from the
feedlot in sealed conveyances to a
recognized slaughtering establishment
for slaughter. While being moved to
slaughter, the bovines must be
accompanied by APHIS Form VS 1–27
or other movement documentation
deemed acceptable by the
Administrator, which must identify the
physical location of the recognized
slaughtering establishment, the
individual responsible for the
movement of the animals, the
individual identification of each animal.
In our January 2007 proposed rule,
however, we proposed to remove each
of the above requirements from the
regulations. The requirements described
above were implemented solely to help
ensure that cattle imported from BSE
minimal-risk regions were slaughtered
at less than 30 months of age—i.e., to
preclude any diversion of the bovines to
other uses in the United States that
would result in a slaughter at some age
30 months or older.
We did not attempt, for that
rulemaking, to assess the BSE risk
associated with the importation of live
bovines 30 months of age or older from
a BSE minimal-risk region. However, as
discussed in our January 2007 proposed
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53347
rule and in this final rule, for this
rulemaking we did assess the BSE risk
associated with the importation of such
animals, and concluded that the
resulting BSE risk from the importation
from Canada of bovines born on or after
March 1, 1999—whether or not the
bovines are 30 months of age or older
when imported and slaughtered—would
be negligible. Therefore, in our January
2007 proposed rule, we proposed to
remove the requirement in § 93.436(a)(1)
of the current regulations that live
bovines imported from BSE minimalrisk regions be less than 30 months of
age when ported into the United States
and when slaughtered.
With the removal of the less-than-30month age restriction on the importation
of bovines from BSE minimal-risk
region, any cattle imported from
Canada—once certification has been
presented to APHIS that the animals
were born on or after March 1, 1999—
will be able to be moved and handled
in the United States in the same way as
U.S.-born cattle.
Scientific evidence strongly indicates
that BSE, unlike most transmissible
diseases of cattle, is not transmitted
from live animal to live animal. BSE is
not a contagious disease and, therefore,
is not spread through casual contact
between animals. Scientists believe that
the primary route of transmission
requires that cattle ingest feed that has
been contaminated with a sufficient
amount of tissue from an infected
animal. Therefore, even a BSE-infected
bovine poses no BSE risk to other
bovines unless those other bovines are
fed BSE-contaminated materials from
the infected animal. This route of
transmission can be prevented by
excluding potentially contaminated
materials from ruminant feed, as is
required in the United States.
If a bovine imported from a BSE
minimal-risk region were diagnosed as
being infected with the disease, from a
biosecurity standpoint, it would not be
necessary to know its record of
movement while in the United States.
However, we would proceed to trace the
bovine back to its herd of origin, in
order to identify birth cohorts of the
animal. Traceback to the animal’s
premises of origin would be facilitated
by the animal’s unique individual
identification, which is required under
the current regulations and continues to
be required by this rule, and which
must be traceable to the premises of
origin of the animal.
Issue: Several commenters stated that
imports of bovines under the proposed
rule should not be allowed until a
mandatory cattle and premises
identification program is implemented
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throughout the United States. At the
minimum, stated one commenter, USDA
should amend the National Animal
Identification System policy to allow for
and integrate with mandatory
identification when required for animal
health programs.
Response: As discussed in the
preceding response, one of the
requirements for the importation of
bovines from BSE minimal-risk regions
is that each animal have unique
individual identification that is not
removed from the animal, except at
slaughter. Such identification is in
addition to any cattle or premises
identification that might be carried out
under the U.S. national animal
identification system, and would
facilitate tracing an imported bovine
that is determined to be infected with
BSE to its herd of origin.
For the reasons discussed above, we
are making no changes based on the
comments regarding the monitoring and
identification of cattle imported into the
United States from a BSE minimal-risk
region.
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Feed Cohorts of BSE-Infected Animals
Issue: Several commenters stated that
the regulations should specifically
prohibit the importation from BSE
minimal-risk regions of feed cohorts of
BSE-infected cattle.
Response: We do not consider it
necessary to add such a provision to the
regulations and are making no changes
based on the comments. Our definition
of a BSE minimal-risk region in § 94.0
of the regulations includes a
requirement that such regions conduct
an epidemiological investigation
following detection of BSE sufficient to
confirm the adequacy of measures to
prevent the further introduction or
spread of BSE, and continue to take
such measures. We described such
investigations in our January 2005 final
rule, as well as in the proposed rule and
the risk analysis for that rulemaking.
This description noted that CFIA
conducts comprehensive
epidemiological investigations, and one
component of these investigations is to
trace feed cohorts of confirmed BSEpositive cattle, in accordance with OIE
guidelines. As a result of these traces,
feed cohorts that remain alive are
euthanized and tested for BSE.
Therefore, since such animals would be
euthanized, there is no need to
specifically prohibit their importation.
Maternal Transmission of BSE
Issue: One commenter stated that
APHIS’ policy of destroying progeny of
BSE-positive cows, in accordance with
OIE guidelines, demonstrates that
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APHIS acknowledges there is some risk
of maternal transmission of BSE. The
commenter expressed the opinion that
APHIS’ conclusion expressed in the
proposed rule that infectivity is unlikely
to localize to the fetal blood is based on
scant scientific evidence that remains
equivocal. The commenter stated that
APHIS does not prescribe any action to
mitigate the additional risk pathway of
the importation of pregnant cattle and
fetuses from pregnant cattle.
Response: We disagree with the
commenter and are making no changes
based on the comment. In the proposed
rule, we pointed out that, based on
scientific and epidemiological data,
maternal transmission of BSE is
unlikely to occur at any appreciable
level. In fact, maternal transmission can
be ruled out in the majority of the cases
born after the 1996 ban in the United
Kingdom of all animal protein from
livestock feed (DEFRA 2007b).
Additionally, modeling studies using
data obtained from the United Kingdom
epidemic show that even if maternal
transmission occurred at very small
levels, it could not sustain an epidemic.
The commenter states that the OIE
continues to recognize the risk of
maternal transmission. However, we
note that the 2006 OIE guidelines
contain no specific recommendations
regarding the destruction of offspring of
infected animals as part of an
epidemiological investigation. These
recommendations were removed after
recognition that the possibility of
maternal transmission is very low. In
addition, the 2006 guidelines with
regard to trade from controlled risk
regions for BSE contain no specific
restrictions regarding progeny of
positive animals. While the 2006
guidelines did contain a restriction for
progeny of positive animals with regard
to trade with undetermined risk regions
(i.e., ‘‘cattle selected for export * * *
are not the progeny of BSE suspect or
confirmed females’’), this reference was
removed in the 2007 OIE general
session. Therefore, all restrictions on the
trade in progeny of BSE-positive
animals have been removed from the
current OIE guidelines. APHIS believes
the weight of the scientific information
and scientific consensus reflected in the
OIE international guidelines support the
conclusion that maternal transmission
of BSE is unlikely to occur at any
appreciable level, and that specific
regulatory measures are not necessary or
warranted.
SRM Removal
Issue: One commenter stated that
USDA regulations should require the
removal of all SRMs from cattle
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imported from Canada at 30 months of
age or older.
Response: FSIS regulations require
the removal of all SRMs from cattle
slaughtered in the United States,
regardless of the country of origin of the
cattle. Therefore, the action requested
by the commenter is already included as
a requirement in USDA regulations for
any cattle 30 months of age or older that
would be imported from Canada.
Ports of Entry
Some commenters addressed the
regulations that have required that live
bovines imported from Canada enter the
United States only through ports of
entries listed as authorized ports in
§ 93.403 of the regulations. Some
commenters expressed concern about
the ability of the ports to handle
shipments from Canada, while other
commenters requested that the list of
authorized ports be expanded.
Authorized Ports of Entry
Issue: Several commenters stated that
the proposed rule should not be
implemented until sufficient personnel,
quarantine facilities, and testing
capabilities are available at the U.S.Canadian border to monitor imports and
detect suspect animals.
Response: APHIS regulations require
that live ruminants imported into the
United States from Canada come
through the border ports listed in
§ 93.403(b) (except as provided in
special cases in § 93.403(f)). APHIS lists
ports in § 93.403(b) only after
determining that they have sufficient
personnel and facilities to accommodate
importations of live animals from
Canada.
Border Ports in Alaska
Issue: Several commenters noted that
none of the border ports listed in
§ 93.403(b) are on the border of Alaska
and Canada and requested that the
regulations provide for such a border
port.
Response: The volume and frequency
of live animal imports through the ports
listed in § 93.403(b) justifies making
Federal inspectors available on a regular
basis. As noted above, § 93.403(f) of the
regulations provides for the designation
by the Administrator of other ports in
special cases as necessary.
Historically, the volume and
frequency of imports of ruminants from
Canada directly into Alaska has not
made it resource-effective to provide the
Federal inspectors for such importations
on a regular basis. Imports of bovines
from Canada into Alaska under this rule
will continue to be handled by special
arrangements on an as-needed basis.
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For the reasons discussed above, we
are making no changes based on the
comments.
Blood and Blood Products
Paragraph (a) of § 94.18 lists regions
from which imports of ruminants and
ruminant products are prohibited or
restricted because of BSE. Those regions
in which BSE is known to exist are
listed in § 94.18(a)(1); those regions that
present an undue risk of introducing
BSE into the United States because their
import requirements are less restrictive
than those that would be acceptable for
import into the United States and/or
because the regions have inadequate
surveillance are listed in § 94.18(a)(2);
those regions that present a minimal
risk of introducing BSE into the United
States via live ruminants and ruminant
products and byproducts are listed in
§ 94.18(a)(3).
The requirements for the importation
of blood and blood products from BSE
minimal-risk regions have been the
same as the requirements for
importation of blood and blood
products from other regions listed in
§ 94.18(a)—only serum and serum
albumin have been eligible for
importation. In our January 2007
proposal, we proposed to allow the
importation of blood and additional
blood products from BSE minimal-risk
regions provided certain conditions
were met regarding the health of the
animal from which the blood or blood
products were derived, or—in the case
of blood collected from a fetal calf—the
health of the dam; the method of
slaughter; the process of collection of
blood; and certification of compliance
with the regulations.
We received comments regarding the
importation of bovine blood and blood
products from BSE minimal-risk
regions. Most of the commenters
addressing this topic expressed concern
regarding such importation, while
others sought clarification as to
allowable methods of collection of
bovine blood intended for importation
as blood or blood products into the
United States.
Issue: Several commenters stated that
the regulations should not allow the
importation of cattle blood for use as
animal feed. One commenter stated that
a number of studies have shown prion
transmission through blood, that there is
evidence that TSE diseases are capable
of crossing the species barrier, that the
EU has banned all animal protein except
meat and eggs from use in feed for any
animal that enters the human food chain
and the United States should do the
same, and that what the commenter
referred to as the EC report on the
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assessment of BSE risk in the United
States specifically condemned the
practice of intraspecies recycling of
ruminant blood and blood products.
Some commenters specifically
expressed concern about the potential
use of blood protein as a milk
replacement or as animal feed, and the
production of spray-dried blood plasma
or blood meal for use in feed.
Response: As we discussed in detail
in our risk assessment, in experiments
examining tissues from BSE-infected
cattle, no BSE infectivity was
demonstrated in cattle blood or any
tested derivatives (EC SSC 2002). Also
as discussed in our risk assessment, the
Scientific Steering Committee of the
European Commission concluded that
the finding of BSE infectivity in the
blood of sheep could not be
extrapolated to BSE in cattle (EC SSC
2002a). Further, the available evidence
indicates that TSEs in other species,
when found in the blood, are localized
primarily to the cellular fractions.
Although BSE has never been detected
in any bovine blood or blood product,
we expect even further risk reduction
after removal of cellular fractions in the
preparation of the most commonly
imported bovine blood commodities. In
addition, the mitigations included in
this rule help prevent contamination of
bovine blood and blood products with
infectious tissues such as SRMs. Thus,
there is no reason to prohibit the
importation of cattle blood for use in
animal feed. (We note that FDA has
responsibility for determining which
materials may be used in animal feed.)
Finally, as discussed in our risk
assessment, infection with BSE via the
oral route is less efficient than by
subcutaneous or intramuscular
injection. Given that we have concluded
that there is a negligible risk for
exposure to bovine blood and blood
products via the injectable route, the
same conclusion holds for exposure via
the oral route.
Issue: One commenter cited a report
(Castilla et al., 2005) regarding the first
detection of scrapie prions in hamster
blood, using a biochemical technique
called protein misfolding cyclic
amplification (PMCA).
Response: APHIS is making no
changes in response to this comment.
The study cited by the commenter does
not present evidence about BSE
infectivity in bovine blood. The cited
study presents a technique for the rapid
amplification and detection of scrapie
prions in hamster blood. The study is
notable because the novel detection
method could be useful in the
development of diagnostic methods.
Previously, only the prion concentration
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53349
in the brain and some lymphoid tissues
was high enough for detection by
routine biochemical detection.
However, APHIS does not assume that
finding the presence of abnormal prion
protein in a given tissue, especially at
low levels, is equivalent to
demonstrating infectivity of the tissue.
APHIS notes that there are very
sensitive bioassays in live animals for
determining the infectivity of various
tissues, such as that for BSE using
intracerebral inoculation of transgenic
mice expressing the bovine PrP. These
methods, recently used by authors of the
cited study and others (Espinosa et al.,
2007; EC SSC 2002) have reliably
determined that, unlike sheep, mouse,
and hamster blood, bovine blood from
BSE-infected animals does not have
demonstrable infectivity.
Issue: One commenter stated that the
reference APHIS used in its risk
assessment in discussing the lack of TSE
infectivity in bovine blood—the
European Commission Scientific
Steering Committee report, 2002—is
dated.
Response: We note that, in addition to
the 2002 European Commission
Scientific Steering Committee report the
commenter refers to, a more recently
published study (Espinosa et al., 2007)
provides evidence of lack of TSE
infectivity in cattle blood. The 2007
study found that orally inoculating
asymptomatic cattle with BSE resulted
in BSE infectivity restricted to the
nervous system, Peyer’s patches, and
tonsils, as had been reported previously
for clinically affected cattle. The study
involved collection of tissue at 20, 24,
27, 30, and 33 months post-challenge.
Infectivity in brainstem and sciatic
nerve was detectable only after 27
months, whereas Peyer’s patches and
tonsils were positive at every time point
tested. Blood, urine, spleen, and skeletal
muscle were negative for detectable
infectivity throughout the study, using
the very sensitive bioassay, intracerebral
inoculation of transgenic mice
expressing the bovine PrP, to assess
infectivity.
Issue: In order to guard against BSE
contamination of blood intended for
importation into the United States from
BSE minimal-risk regions—or blood
products derived from such blood—we
proposed to require that the blood be
collected in a closed system (in which
the blood is conveyed directly from the
animal in a closed conduit to a closed
receptacle) or in an otherwise hygienic
manner that prevents contamination of
the blood with SRMs.
Several commenters stated that,
because of current line speeds in beef
slaughter facilities, a closed collection
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system is not practical and would be
cost prohibitive for production of spraydried blood plasma or blood meal. The
commenters stated that industry
associations of both renderers and
spray-dried blood and plasma producers
in the United States and Canada have
developed and implemented guidelines
and a code of practice designed to
minimize the risk of contamination. One
of the commenters stated that the
manufacture of spray-dried blood
products involves concentration of the
liquid plasma with reverse osmosis or
ultra-filtration, followed by atomization
of the concentrated liquid in a heated
drying container. According to the
commenter, because the filtration and
spray drying equipment will operate
inefficiently if the feed liquid contains
particulate material, a number of prefiltration steps to remove particulate
contamination are included in the
production of spray-dried blood
products. The commenter stated that the
combination of the filtration system
with manufacturing standards results in
a system that meets the requirements of
the regulations for collection ‘‘in an
otherwise hygienic manner that
prevents contamination of the blood
with SRMs.’’
Several other commenters
recommended that the regulations
specifically provide for the adoption of
alternative, less restrictive mitigation
measures should the Administrator
determine they are scientifically
justified.
Response: As noted above, our
proposed rule provided for collection in
an otherwise hygienic manner that
prevents contamination of the blood
with SRMs, in lieu of using a closed
system for the collection of blood.
APHIS will determine whether an
alternative process collects blood in a
hygienic manner that prevents
contamination of the blood with SRMs
upon request by a party that such a
determination be made. The request for
determination must include a
description of the proposed alternative
method of collection.
Based on information received from
the industry and an evaluation of
industry capabilities, APHIS would
consider the following to be an example
of an acceptable alternative collection
process at a slaughter facility: After the
animal has passed ante-mortem
inspection and is stunned, a long
midline cut is made in the skin on the
ventral part of the neck. A specially
designed bucket—with two barbs that
allow it to hang on the hide and that has
been treated with anticoagulant prior to
use—is inserted into the cut, so that the
opening of the bucket, an oval-shaped
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area that conforms to the shape of the
cut, is essentially inside the skin. As the
animal moves down the line, another
cut is made with a clean knife inside the
skin opening, cutting the arteries and
veins through the thoracic inlet for
exsanguinations. The carcass travels
down the rail while the blood drains.
The bucket is mechanically removed by
a conveyor at the end of this line. The
conveyor carries the bucket into a
separate room (separate from the kill
floor), and empties the bucket into a vat
with a screen to pick out any clots. The
blood in the vat is then centrifuged, and
the cells are piped to a dryer in another
part of the plant, while the plasma is
held in large refrigerated vats prior to
transfer to another processing facility.
The empty bucket travels through a prewash that removes any remaining blood,
then through a disinfectant wash. Before
reentering the collection process, the
cleaned and disinfected bucket is
treated with a measured amount of
anticoagulant.
For the reasons discussed above, we
are making no changes based on these
comments to the proposed requirements
for importing blood or blood products.
Small Intestine
The regulations in § 94.19 have
required that meat, meat byproducts,
and meat food products derived from
bovines that have been in a BSE
minimal-risk region be derived from
bovines from which the SRMs and the
small intestine were removed at
slaughter. The regulations at § 95.4(g)
have applied this same requirement to
offal derived from bovines from BSE
minimal-risk regions. Section 94.0
defines SRMs as ‘‘those bovine parts
considered to be at particular risk of
containing the bovine spongiform
encephalopathy (BSE) agent in infected
animals, as listed in the FSIS
regulations at 9 CFR 310.22(a).’’
The regulations require removal of the
entire small intestine, even though only
part of the small intestine (the distal
ileum) has been determined to be an
SRM, to ensure removal of the distal
ileum.
In our January 2007 proposed rule, we
proposed to remove the requirements
for removal of the entire small intestine.
We proposed, instead, to require
removal of 80 inches of the uncoiled
and trimmed small intestine, as
measured from the cecocolic junction,
unless the processing establishment has
demonstrated that an alternative method
is effective in ensuring complete
removal of the distal ileum. We
explained that this proposed change is
consistent with the definition of SRMs
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in the FSIS regulations at 9 CFR
310.22(a).
Some commenters who addressed the
topic of the removal of the distal ileum
and other parts of the small intestine
requested that the regulations be made
more stringent than at present, while
others expressed the view that our
proposed regulations were too
restrictive.
Issue: Several commenters addressed
our proposed change regarding removal
of the small intestine. One commenter
recommended not only that the
regulations continue to require the
removal of the small intestine, but that
we require that the large intestine be
removed as well. The commenter stated
that the European Commission
Scientific Steering Committee stated
that, because slaughterhouse
contamination of other intestinal areas
with matter from the distal ileum cannot
be avoided, it is prudent to remove the
entire small and large intestines.
Additionally, stated the commenter, the
International Review Team (IRT) that
issued a report to the U.S. Secretary of
Agriculture in February 2004 called for
the banning the entire intestine—from
anus to pylorus—from human and
animal food, from cattle of any age.
Response: The issue of how much of
the intestines should be removed to
ensure removal of the distal ileum to
prevent contamination with the BSE
agent was also raised in response to
rulemaking documents published in the
Federal Register by FSIS and FDA. The
agencies’ responses to those comments
were published in interim final rules
published in the Federal Register on
September 7, 2005. (FSIS Docket No.,
03–025IFA, 70 FR 53043–53050, and
FDA Docket No. 2004N–0081, 70 FR
53063–53069). We concur with FSIS
and FDA that, although the EU prohibits
the entire intestine from use in food, the
data we are aware of indicating BSE
infectivity along the entire intestine is
from other species, and may not
represent the distribution of infectivity
in cattle infected with BSE, as
evidenced by studies with bovine
tissues.
In cattle, infectivity has been found in
the distal ileum in tissue assay from
cattle experimentally given BSE (Wells
et al., 1994). In such cattle, positive
Peyer’s patches were found by
immunohistochemistry only in the
distal ileum, and in cattle with naturally
occurring and experimental BSE,
positive myenteric plexus neurons were
found only in the distal ileum (Terry et
al., 2003). The duodenum of cattle
experimentally given BSE has not
demonstrated infectivity when tested by
mouse bioassay and has been negative
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for the presence of abnormal prions
when examined by
immunohistochemistry during all stages
of the pathogenesis of the disease
(Wells, 1994). Few samples of jejunum
have been tested, but those that have
been tested were negative for the
presence of abnormal prions when
examined by immunohistochemistry
(Terry et al., 2003). In a bioassay of
tissues from cattle with naturally
occurring BSE, no infectivity was found
in the splanchnic nerve, rumen,
omasum, abomasum, proximal small
intestine, proximal colon, distal colon,
and rectum, or in the distal small
intestine (EU SSC 2002).
The study by Terry and others
indicated that the myenteric plexus of
the distal ileum contained some
abnormal prion protein in neurons
(Terry et al., 2003). Since the myenteric
plexus extends throughout the small
intestine, we acknowledge the
possibility that infectivity might exist in
the myenteric plexus of the jejunum or
the duodenum. However, if infectivity
in intestinal tissues (other than distal
ileum) exists, it is below the level of
detection by both mouse and cattle
bioassay. Given the relative efficacies of
these experimental modes of
transmission compared to oral exposure
at doses estimated to have occurred in
the field, we conclude that intestine
other than the distal ileum is highly
unlikely to contain epidemiologically
significant levels of infectivity, if any
infectivity is present at all.
We do not agree that slaughterhouse
contamination of other intestinal areas
with matter from the distal ileum cannot
be avoided. FSIS is responsible for
ensuring the adequacy and effectiveness
of procedures for removing the distal
ileum in slaughterhouses. The FSIS
regulations require that establishments
develop, implement, and maintain
written procedures for the removal,
segregation, and disposition of SRMs,
and that they incorporate these
procedures into their HACCP (Hazard
Analysis and Critical Control Point)
plans, sanitation standard operating
procedures, or other required programs
(9 CFR 310.22(d)(1)). These procedures
must ensure that SRMs, including the
distal ileum, are completely removed
from the carcass, segregated from edible
products, and disposed of in an
appropriate manner as prescribed by 9
CFR 314.1 and 9 CFR 314.3 (i.e., used
for inedible rendering, incinerated, or
denatured). Regions wishing to export
meat and meat products to the United
States must follow processing practices
equivalent to those of FSIS.
With regard to the IRT report
referenced by the commenter, the
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recommendation for removal of the
entire intestine, from anus to pylorus,
was meant to apply in the United States
only if the risk of BSE had not been
determined to be minimal, based on
aggressive surveillance. Aggressive
surveillance conducted in both the
United States and Canada indicate a
very low prevalence of BSE. Therefore,
the recommendation of the IRT for
removal of the entire intestine of all
cattle does not apply. As discussed
above, scientific evidence does not
support the designation of the entire
intestine as an SRM.
Issue: Several commenters stated that
the regulations should require that only
the distal ileum be removed, rather than
an additional 80 inches of small
intestine. The commenters stated that
APHIS has not established that it is
necessary to excise so much additional
intestine. At a minimum, stated the
commenters, the regulations should
allow the Administrator to approve
effective alternatives in ensuring
complete removal of the distal ileum.
Response: As discussed in our
proposed rule, removal of the distal
ileum as well as an additional portion
of the small intestine is consistent with
FSIS and FDA requirements to ensure
removal of the distal ileum. APHIS
concurs with FSIS and FDA that, unless
demonstrated otherwise, to ensure
complete removal of the distal ileum, it
is prudent to require removal of 80
inches of the uncoiled and trimmed
small intestine as measured from the
cecocolic junction. We concur that this
standard will ensure removal of the
distal ileum despite differences in
length of the intestinal tract or its
segments between breeds or variations
from animal to animal of the same
breed. However, we recognize, as do
FSIS and FDA, that alternative means of
ensuring removal of the distal ileum
may exist, and current APHIS
regulations provide for such alternative
means.
For the reasons discussed above, we
are making no changes based on these
comments to the proposed requirements
regarding removal of part of the small
intestine.
Bovine Tongue
Issue: One commenter stated that
USDA’s assumption that removal of a
fraction of the small intestine and the
tonsils removes any potential for
transmission to humans is unjustified,
given that APHIS has not evaluated the
potential for contamination of tongue
with tonsil tissue. The commenter also
stated that APHIS claims this possibility
is eliminated by current slaughter
techniques, and stated further that such
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53351
an assumption is contradicted by facts
(i.e., scientists who examined over 250
bovine tongues intended for human
consumption found tonsillar tissue in
the vast majority—in some cases, ‘‘even
after the most rigorous trimming of the
root of the tongue’’ (Wells et al., 2005).
The commenter stated that APHIS
cannot simply assume this risk away by
stating, without record support, that it is
eliminated.
Response: We are making no changes
based on the comment. Wells et al.
(2005) state the following:
However, the trace level of infectivity so
far detected in tonsillar tissue and the
localization of the lingual tonsillar lymphoid
tissue, together with the current SRM
legislation for the removal of tonsil from
cattle carcasses and the low and diminishing
prevalence of BSE in the UK suggest that the
risk of human exposure to infected tonsil is
now remote. It seems likely that under these
circumstances any additional trimming of the
tongue would result in an immeasurable
reduction in the risk. * * *
In other words, the study cited by the
commenter does not present a strong
case for additional risk measures. The
study, in fact, indicates the opposite
conclusion.
Moreover, even before the SRM
requirements were implemented in
January 2004, FSIS did not consider
tonsil to be edible tissue—it was
previously required to be removed. As
noted in FSIS Notice 50–04:
In the preamble to 9 CFR 310.22, FSIS
stated that tonsils of all livestock species,
including cattle, were already required to be
removed and were prohibited for use as
ingredients in meat food products under 9
CFR 318.6(b)(6). The accepted practice for
removing the tonsils from livestock has been
to remove all visible tonsils. In cattle, this
includes separation of the palatine tonsils
and lingual tonsils from the tongue (in
establishments that harvest the tongue for
human food) by a transverse cut caudal (just
behind) the last vallate papillae. * * * FSIS
expected that establishments would continue
to remove tonsils from cattle in accordance
with the procedures that they had
implemented to comply with 9 CFR
318.6(b)(6) * * *. Establishments that
slaughter cattle should have been following
these practices before tonsils were designated
as SRMs. (FSIS, 2004).
APHIS’ quantitative exposure model
included an update that acknowledged
the potential infectivity in tonsils and
clearly added these as an SRM, with the
acknowledgment that they could still be
potentially available for human
consumption. In fact, the output tables
from the model runs show the potential
ID50s derived from tonsils and available
for human consumption over the 20year period of the analysis. These values
are obviously very low, ranging from
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0.026 ID50s in the base case scenario to
0.16 ID50s in sensitivity analysis 6 (in
which all uncertain parameters were
simultaneously set to their
corresponding pessimistic level). Such
very small values are not surprising
given the low likelihood of infectivity in
the tissue itself. These possible
exposure routes were therefore
explicitly modeled and not ‘‘assumed
away.’’ Moreover, although our model
predicts a vanishingly low level of
possible human exposure via tonsils, we
have not stated that the risk is
‘‘eliminated,’’ as was suggested in the
comment.
Issue: A number of commenters urged
that, before this rule is implemented, a
plan should be in place for the removal
and mitigation of any potential risk
factors that might arise from the
introduction of the BSE agent into the
United States because of the importation
of a BSE-infected cow.
Response: We are making no changes
based on the comments. The safeguards
in the United States regarding any BSEinfected cow that might be imported
from a BSE minimal-risk region are the
same that are in place to deal with a
BSE-infected cow of any source,
including any of U.S. origin that might
be detected. These mitigations are
simulated in the quantitative exposure
model used in the risk assessment for
this rule.
The primary animal-health mitigation
measure is the feed ban implemented by
the FDA in 1997. This feed ban is the
most important measure to prevent the
transmission of disease to cattle. In
addition to the regulatory restrictions
imposed by the feed ban, other industry
practices—such as rendering processes
that inactivate a significant proportion
of BSE infectious agent present in raw
material—and biological processes—
such as age susceptibility to infection—
also help to mitigate the transmission of
disease to animals.
Public or human health protective
measures are maintained by both the
FSIS and the FDA. The most important
public health protective measure is the
removal from the human food supply of
SRMs. Other controls include
prohibiting air-injection stunning of
slaughter cattle; requiring additional
process controls in advanced meatrecovery systems; forbidding the use of
mechanically separated meat in human
food; and prohibiting nonambulatory
disabled cattle from the human food
chain. Additionally, protection from
BSE and other disease is achieved
through ante-mortem inspection of
slaughter cattle and the exclusion of
animals with any clinical signs of
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neurological disease or other
abnormalities.
If a BSE-positive bovine were
identified in the United States, APHIS
would lead an epidemiological
investigation that would include the
tracing of birth cohorts of the infected
animal. Birth cohorts are those animals
that could have been exposed to the
same feed as the infected animal, and
include those bovines that were born on
the same premises as the infected
animal during the 12-month period
immediately before the birth of the
infected animal or during the 12-month
period immediately after the birth of the
infected animal. They would also
include other bovines raised on the
premises at the time the infected animal
was there. Any birth cohorts located
would be prevented from entering the
human or animal feed chains. In
addition to the APHIS epidemiological
investigation, FDA would conduct an
extensive feed investigation to help
determine the potential source of the
infection.
With regard to commodities eligible
for importation from BSE minimal-risk
regions under this rule, we have
concluded that such commodities can
be imported with a negligible BSE risk
to the United States.
The Role of States
Several commenters discussed the
role U.S. States should play regarding
bovines imported from BSE minimalrisk regions.
Issue: Commenters stated that CFIA
and APHIS should provide the State
veterinarian in the U.S. State that is
receiving such bovines with all animal
health and identification documentation
before the animal is imported.
Commenters requested further that the
regulations require all importers of
cattle over 30 months of age from BSE
minimal-risk regions to report all
movements of the animal to the
department of agriculture of the
recipient State before the animal is
moved into or through the State.
Response: As noted above, the
purpose of the current APHIS
regulations with regard to BSE, and
those in this rule, is to allow the
importation into the United States of
commodities that can be imported with
a negligible likelihood of the BSE
exposure and establishment in the U.S.
cattle population as a consequence of
eligible imports from Canada. We do not
consider the extensive recordkeeping
and paperwork requirements suggested
by the commenters to be warranted or
justified by science and are making no
changes in response to the comments.
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Issue: Commenters recommended that
APHIS authorize each State Veterinarian
to ensure that the animal health and
identification requirements of the
APHIS regulations are met, and
recommended further that, in the event
the State determines noncompliance
with the APHIS regulations, USDA
support the enforcement actions of the
State officials.
Response: APHIS has a historical and
ongoing working relationship with State
animal health officials to protect
livestock in the United States from both
foreign diseases and diseases endemic
to the United States. This ongoing
cooperation has enabled the United
States to protect this country’s livestock
from a variety of diseases, including
BSE. It has not been necessary to specify
this working relationship in the APHIS
regulations, and we do not consider it
warranted to do so for any one disease.
However, APHIS emphasizes that it
values highly its cooperative efforts
with State animal health officials and
welcomes a continuing exchange of
information and support in carrying out
our mutual missions.
Potential Economic Effects of the
Proposed Rule
A large number of commenters
addressed the potential economic effects
of the proposed rule. Most of these
commenters expressed concern that the
proposed rule would have an
unacceptable negative impact on U.S.
entities. Some of the commenters took
issue with the economic analysis we
conducted for our proposed rule.
Issue: Many commenters
recommended that APHIS withdraw or
restrict implementation of this rule
because of its potential negative
economic effects on the U.S. livestock
and livestock product industry, due to
the potential significant influx of cattle
from Canada over a short period of time.
A number of commenters requested that
the rule not take effect until USDA has
developed and implemented an orderly
market transition plan to reduce the
negative effect of the rule on U.S. cattle
producers. One commenter stated that
such a plan should include gradually
accepting imports, so as not to overload
the U.S. cattle supply and crash those
markets. Further, commenters
recommended that APHIS delay
implementation of the rule until all U.S.
export markets that were closed due to
the December 2003 detection in an
imported cow in Washington State are
reopened.
Response: APHIS does not have the
statutory authority to restrict trade
based purely on its potential economic
impact, market access effects, or
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quantity of products expected to be
imported. Under the Animal Health
Protection Act, the Secretary of
Agriculture may prohibit or restrict the
importation or entry of any animal or
article when the Secretary determines it
is necessary to prevent the introduction
or dissemination of a pest or disease of
livestock. This authority has been
delegated to APHIS.
We note that this rule, and our
January 2005 final rule, do not make any
commodities eligible for importation
from Canada that were not already
allowed importation prior to May 2003,
when a BSE-infected cow was
diagnosed in Canada. One difference
between the current situation and preMay 2003, however, is that certain of
the commodities that are now eligible
for importation, or that will become
eligible when this rule becomes
effective, are subject to risk mitigating
importation conditions appropriate to
the fact that BSE has been detected in
Canada and that we consider that
country a minimal-risk region for BSE.
As noted above, both Canada and the
United States have been classified as
controlled risk countries for BSE under
the OIE guidelines. Additionally, even
under these rules, there are some
commodities (e.g., cattle born before
March 1, 1999) that continue to be
ineligible for importation into the
United States. Nevertheless, this
rulemaking and our January 2005 final
rule represent to a great extent a return
to trade patterns that existed between
the United States and Canada for many
years previously. As discussed in the
January 2007 proposal for this rule, in
this final rule, and in the risk
assessment for this rule, we have
determined that the commodities
eligible for importation from Canada
under this rulemaking can be imported
into the United States under the
conditions specified with a negligible
BSE risk to the United States.
With regard to exports markets that
were closed to U.S. beef following the
December 2003 detection of BSE in a
cow of Canadian origin in Washington
State, U.S. Government agencies are
actively negotiating with trading
partners to reestablish our export
markets. After the 2003 detection of an
imported BSE-infected cow in
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Washington State, many of the 114
nations that imported U.S. beef banned
our beef and live animals, despite the
apparent lack of scientific basis for such
measures. The efforts of multiple U.S.
Government agencies have succeeded in
removing bans in over half of those
markets, including our largest export
market, Japan. U.S. Government
agencies continue to work to reopen or
further open markets where restrictions
remain; the results of these negotiations
are posted on the USDA APHIS Web site
(https://www.aphis.usda.gov).
Issue: Some commenters took issue
with the economic analysis that we
conducted for our January 2007
proposed rule. One commenter stated
that the economic analysis ignored any
multiplier effects (i.e., the impact of a
change in the level of economic activity
in one sector on other sectors of the
economy and on households in terms of
employment and income) that would
come from the broader economic
impacts on the beef wholesale sector.
Response: We used the multi-sector
model in our economic analysis to
examine impacts for the major vertically
linked marketing channels for beef and
other livestock products. We estimate
consumer surplus for the beef sector
will increase by 1 to 1.3 percent at the
retail level in scenario 3 of the economic
analysis. Indirect downstream effects on
income and employment are not
modeled; however, we do not believe
APHIS is required to analyze the
impacts of regulation on every sector of
the economy that may be indirectly
affected by these changes. As in many
regulations, opportunity costs imposed
on one sector of the economy are often
passed on to other sectors of the
economy. We anticipate that there may
be indirect economic benefits to
communities where, for example, cull
cattle imported from Canada result in
increased slaughter plant employment.
In other communities, there may be
income and employment losses due to
reduced spending by producers who
face a fall in prices for cull cattle. These
impacts are expected to be small on a
national basis, although they may show
some geographic concentration. Overall,
the effects of this rule are expected to
reflect a return to trade circumstances
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53353
similar to those that existed prior to
May 2003.
Issue: One commenter indicated that
APHIS acknowledged the sensitive
nature of the results of the economic
analysis based on the parameters
(elasticities) used to drive the economic
model and requested public comment
on those parameter assumptions. The
commenter stated that APHIS should
have done a literature search for studies
that report on these parameters and
should have made those reported
parameters available, in order to provide
policy analysts with fuller knowledge to
assess the accuracy of the results
reached by APHIS.
Response: APHIS agrees that this
would be useful information to provide
for those interested in the impact
analysis. The two tables that follow
summarize our overview of demand and
supply elasticities estimated or used in
published research. The referenced
sources are identified in a footnote
following the tables.12 The elasticities
we use in the economic analysis fall
within a reasonable range of the
elasticities found in these various
sources.
12 Arnade, C.,and K. Jones. ‘‘Modeling the Cattle
Replacement Decision.’’ Paper prepared for
presentation at the American Agricultural
Economics Association Meeting, Montreal, Canada,
July 27–30, 2003.
Brester, G.W., J.M. Marsh, and V.H. Smith. ‘‘The
Impacts on U.S. and Canadian Slaughter and Feeder
Cattle Prices of a U.S. Import Tariff on Canadian
Slaughter Cattle.’’ Can. J. Agr. Econ. 50(March
2002), pp. 51–66.
Brester, G.W. ‘‘Estimation of the U.S. Import
Demand Elasticity for Beef: The Importance of
Disaggregation.’’ Rev. Agr. Econ. 18(January 1996),
pp. 31–42.
Brester, G.W., and M.K. Wohlgenant. ‘‘Estimating
Interrelated Demands for Meats Using New
Measures for Ground and Table Cut Beef.’’ Amer.
J. Agr. Econ. 73(November 1991), pp. 1182–94.
Marsh, J.M. ‘‘Impacts of Declining U.S. Retail
Beef Demand on Farm-Level Beef Prices and
Production.’’ Amer. J. Agr. Econ. 85(November
2003), pp. 902–13.
Marsh, J.M. ‘‘Estimating Intertemporal Supply
Response in the Fed Beef Market.’’ Amer. J. Agr.
Econ. 76(August 1994), pp. 444–53.
Marsh, J.M. ‘‘USDA Data Revisions of Choice Beef
Prices and Price Spreads: Implications for
Estimating Demand Responses.’’ J. Agr. and Res.
Econ. 17(December 1992), pp. 323–34.
Wohlgenant, M.K. ‘‘Demand for Farm Output in
a Complete System of Demand Functions.’’ Amer.
J. Agr. Econ. 71(May 1989), pp. 241–52.
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Issue: One commenter stated that the
type of ‘‘welfare’’ analysis APHIS used
in its economic analysis is invalid
because it relies upon the unscientific
concept of interpersonal utility
comparison.
Response: We disagree. Our economic
analysis does not attempt to make
interpersonal utility comparisons. We
recognize that an additional dollar of
income provides a different level of
utility to every individual. APHIS uses
techniques that are quite standard in
welfare and trade economics; we
estimate changes in consumer and
producer surplus that may result from
projected changes in cattle and beef
imports from Canada under different
scenarios. For a given transaction,
consumer surplus refers to the value
that the purchase of the good provides
the buyer over and above its price.
Producer surplus refers to the value that
the sale of the same good provides the
seller over and above the lowest price at
which he would have been willing to
sell it.
The estimated changes in welfare and
prices are generalized across all entities
that would take part in transactions
concerning the particular commodity at
hand, such as the purchase and sale of
cull cattle. We make no attempt to
evaluate impacts on income distribution
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or the utility gained or lost by
individual market participants. In a
transaction, the buyer and the seller
both gain utility, as individually
determined, compared to their next best
alternatives. Otherwise the transaction
wouldn’t occur. But for some entities,
the ‘‘gain’’ in utility may be, in fact, a
smaller welfare loss than the participant
anticipates would be incurred without
the transaction (e.g., selling a cull
animal rather than keeping it past the
optimal point of sale, even though the
price has declined). Commodity-wide
changes in welfare (changes in
consumer and producer surplus) reflect
the changes in utility across all buyers
and sellers of the commodity.
The common measure of value and,
therefore, of changes in welfare is, of
course, the dollar. Our analysis
appropriately uses changes in consumer
and producer surplus, expressed in
dollars, to evaluate net benefits of this
rule and other scenarios considered. As
pointed out in the Office of Management
and Budget’s Circular A–4, a distinctive
feature of benefit-cost analysis is that
both benefits and costs are expressed in
monetary measures, which allows a
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common measure for evaluation of
different regulatory options.13
Issue: One commenter stated that the
economic analysis for the proposed rule
is invalidated by its assumption that
import numbers will be exogenous,
rather than determined within the
context of a dynamic North American
livestock market.
Response: APHIS disagrees. We agree
that the North American livestock
market is a dynamic system, with the
interplay of changing prices and
changing supply and demand quantities
continually redefining market
equilibria. The projected imports from
Canada may be exogenous to the
particular model we used to estimate
domestic impacts; however, they are
derived from USDA baseline projections
and anticipated market changes that
reflect the fluidity of interacting
markets. In other words, the impacts
were not modeled as external exogenous
shocks, but rather as rational responses
to changing market conditions. We also
note that every model is an abstraction
from reality that relies upon selected
exogenously determined values and
parameters. Our import projections are
13 Office of Management and Budget, Circular No.
A–4, Regulatory Analysis, September 17, 2003.
https://www.whitehouse.gov/omb/circulars/a004/a4.pdf
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well based in theory and market
considerations. Imports of Canadian cull
cattle will be newly reestablished by the
rule, and effects for the other modeled
commodities will derive from the
resumption of the cull cattle imports.
The principal model we use to evaluate
expected effects of the rule is a net trade
model, and its operation is driven by
projected changes in net trade.
Issue: One commenter stated that our
economic analysis overstates consumer
benefits associated with the availability
of cull cattle for slaughter in the United
States, because it does not adequately
account for substitution among the
modeled products in both the United
States and Canada.
Response: Consumer welfare benefits
are expected to be gained under the rule
by buyers of processing beef at the
wholesale level. Lean processing beef
from cull cattle and trimmings from fed
beef are complementary goods that are
combined to produce ground beef. At
the level of the retail shopper, there is
a degree of substitution between ground
beef and fed beef cuts, but this
relationship is not expected to
significantly influence the estimated
consumer benefits attributable to the
rule.
As part of the economic analysis for
the final rule, we simulate substitution
among livestock products in response to
relative price changes. The simulations
yield measures of consumer welfare
changes at the retail level. Results of
this analysis indicate that, with the rule
under scenario 3 as discussed in our
economic analysis and in the summary
of that analysis in this document (entry
of Canadian cattle born on or after
March 1, 1999, and resumption of
imports of beef from Canadian cattle
slaughtered at 30 months of age or
older), consumer surplus for the beef
sector at the retail level will increase by
1 to 1.3 percent compared to a 2006
baseline.
Issue: One commenter stated that,
based on normal culling rates, the
January 2007 herd size, the
modernization and expansion of
Canada’s slaughter plants, and the
increased use of Canadian beef in the
Canadian domestic market, the number
of animals that might be available for
export is considerably lower than the
number estimated by USDA. The
commenter calculated that the number
of older, age verified, beef and dairy
animals that might be eligible for export
would total about 471,000 head
annually, consisting of approximately
250,000 dairy cows, 154,000 beef cows,
and 67,000 bulls. The commenter noted
that the estimate of 471,000 head should
be viewed as an upper bound and that,
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if confirmation of an animal’s age
proves to be a complex procedure, that
number would be reduced.
One commenter stated that, in
assessing the potential economic effects
of this rulemaking, the use of any
historical references regarding trade
flows and regional basis levels to assess
potential impacts are not likely to be of
much use, due to changes in cattle
usage. The commenter stated that the
vast majority of Canadian cull cows and
bulls will be converted into beef in
Canada, and, after subtracting the
elimination of the supplemental tariff
rate quota (TRQ) supplies, the balance
could be exported to the United States
depending on the influence of the
exchange rate. (‘‘TRQ’’ is the total
annual quantity of a commodity that can
be imported at a lower tariff rate,
excluding imports from NAFTA
countries. Canada’s supplemental TRQ
beef supplies were quantities of beef
above the tariff rate quota that were
allowed by Canada to enter at the lower
tariff rate. In eliminating supplemental
TRQ certificates—that is, by not
allowing additional beef imports at a
lower tariff rate, Canada is relying to a
greater extent on domestic production
and less on imports.)
Response: We have considered these
observations carefully and reassessed
the proposed rule import projections
and, as a result, have revised our
economic analysis based on a smaller
quantity of cull cattle projected to be
imported from Canada. Although the
modernization and expansion of
Canada’s slaughter plants and increased
reliance on Canadian beef in the
Canadian domestic market will tend to
dampen cull cattle imports from that
country, we expect the major reason for
a smaller number of imports will be the
requirement that the cattle be verified as
having been born on or after March 1,
1999. In the preliminary regulatory
impact analysis (RIA) we conducted for
our January 2007 proposed rule, we
projected that cull cattle imports from
Canada in 2008, for example, would
total 657,000 head (586,000 cows and
71,000 bulls and stags). In scenario 3 of
the final RIA, however, we are
projecting cull cattle imports in 2008
totaling 75,000 head (63,000 cows and
12,000 bulls and stags). We believe that
the commenter who estimated that there
would be approximately 471,000 older
cattle eligible for import from Canada,
and who acknowledged that number
was an upper bound estimate, did not
fully consider the extent to which the
age verification requirement would
reduce the number of eligible cattle. Of
the cull cattle that might be imported by
the United States if there were no age
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restriction and no age verification
requirement, only about one-fourth are
expected to be eligible for importation
in 2008 under this rule, and only about
one-half may be eligible by 2012.
Issue: One comment stated that
APHIS did not provide an explanation
in its economic analysis for the different
percentages of cattle over 30 months of
age and of such cattle plus beef from
cattle over 30 months of age assumed to
displace other processing beef imports.
Response: We agree that it is
reasonable to expect, for all of the
scenarios set forth in the economic
analysis, that a consistent percentage of
Canadian imports across the scenarios
would displace other imports. We have
revised the final RIA accordingly. In this
final rule, we estimate that 25 percent
of cull cattle imports from Canada
(scenarios 1 and 2 in our economic
analysis) and 25 percent of cull cattle
and beef derived from cattle 30 months
of age or older (OTM beef) from Canada
(scenario 3 in our economic analysis)
will displace U.S. processing beef
imports from elsewhere. The estimate of
25 percent comes from simulations of
the multi-sector model and takes into
account interactions of the processing
beef sector with the beef cattle and dairy
cattle sectors. The model allows cattle
prices to adjust to an increase in beef
imports from one source (in this case,
cull cattle and OTM beef imports from
Canada), spreading the market response
across both beef and cattle. This
interaction dampens the beef price
decline and reduces the amount of
displacement below that would be
expected to occur by considering only
the market for processing beef. We also
examine the sensitivity of the impacts to
changes in the quantities of cull cattle
and processing beef imported from
Canada that displace processing beef
from elsewhere: The RIA presents
results assuming 50 percent of the
imports from Canada displace imports
from elsewhere as well as results
assuming none of the imports from
Canada displace other imports.
Issue: Several commenters, in
addressing the potential economic
effects of this rulemaking, stated that the
time of year a final rule would go into
effect is an extremely important variable
in assessing its initial economic impact.
One commenter stated that U.S. cull
cow marketings are highly seasonal
because the majority of calves are born
in the spring and the decisions to retain
cows are generally made during the fall.
As a result, the months of October,
November, December, and January are
typically lowest for cull cow prices.
Another commenter stated that
implementation of the rule in the fall of
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2007 (post-weaning) would likely result
in a larger impact on U.S. cull cow
prices in the very short term.
Response: We agree with the
commenters that, in the short term, the
timing of the resumption of imports of
cull cattle and processing beef from
Canada could have an impact on
producers’ monthly revenues.
Historically, cull cow slaughter in the
United States is highest in the months
of October, November, December, and
January. As the commenters noted,
because of this, cull cow prices are
typically lower in these months.
Limited data prevent analysis on a
monthly basis of price changes in
response to projected cull cattle imports
from Canada. However, we do
acknowledge that, because of the larger
number of cull cattle marketed per
month, during October through January,
a slight price decline during this period
would result in larger total monthly
revenue losses for U.S. producers than
during the other months of the year.
This seasonal difference in monthly
revenue losses would not be large on an
annual basis.
This outcome is demonstrated in
research conducted at Montana State
University (Brester et al., 2007). This
study examined effects of additional
cull cattle slaughter using two scenarios:
One in which Canadian cull cattle
imports return to pre-2003 levels and do
not displace beef imports from other
countries, and a second in which 50
percent of cull cattle and processing
beef imports from Canada displace beef
imports from Uruguay. The changes in
U.S. cull cattle prices estimated for
these two scenarios are declines of $1.55
per cwt and $0.78 per cwt, respectively.
The average of the price changes
reported in the Montana State study,
$1.17 per cwt (2.5 percent of the 2006
average U.S. cull cow price of $47.56
per cwt), would correspond to 25
percent of imports from Canada
displacing processing beef imports from
other countries, which is the percentage
share used in the economic analysis for
this final rule.
As reported by Brester et al. for the
period, 2000–2006, monthly cull cattle
sales averaged 488,000 head, October
through January, compared to an
average of 434,000 head per month,
February through September. Based on
the Montana State study results, a 25
percent level of displacement would
correspond to a decrease in total
monthly revenue for cow-calf producers
of $5,956,500, October through January,
and $5,297,000, February through
September. In other words, there would
be an additional revenue loss of
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$659,000 (12 percent) per month,
October through January.
We project in our economic analysis
a baseline for beef and dairy cow
slaughter in 2008 totaling 5,084,000
head, and a nominal 2008 price of
$54.19 per cwt. Based on an average live
slaughter weight of 1,050 pounds, total
baseline gross revenue from the sale of
cull cows in 2008 would be $2.89
billion. The increase in producer losses
because of increased cull cattle sales
occurring during the months of October
through January, rather than during the
months of, February through September,
based on the Montana State study
results, would total less than 0.1 percent
of the projected baseline annual revenue
from cow slaughter.14
While we recognize that the timing of
the resumption of cull cattle imports
from Canada may influence the size of
the short-term impacts for producers,
differences in revenue losses due to the
timing of the implementation of the rule
are considerably smaller when
considered on an annual basis. Our
analysis is in terms of annual cattle
import projections and, therefore, yields
annual price and welfare effects. The
within-year distribution of effects is
smoothed in the annual estimate.
Issue: Many commenters addressed
the issue of the potential economic
impact on U.S. cattle producers should
a bovine of Canadian origin be
diagnosed in the United States as BSEinfected. A number of the commenters
expressed general concern regarding
such a potential impact, and suggested
that APHIS’ analysis of the potential
economic effects of the proposed rule
was incomplete because it did not
consider such impacts. Commenters
stated that such impacts have been large
in other countries and could overwhelm
the effects estimated by APHIS if a BSEinfected animal imported into the
United States under the provisions of
this rule caused the spread of BSE in the
United States, and that a comprehensive
economic analysis should include
consideration of the demand reactions
that would be triggered by identification
of additional Canadian-born BSE cases
in the United States, even at the low
levels projected in APHIS’ risk
assessment.
Other comments stated that the cost
associated with the projected
14 An additional revenue loss of $659,000 per
month, October through January, multiplied by the
four months, yields an additional annual revenue
loss of $2,636,000. This amount divided by the total
baseline revenue from cow slaughter projected in
the regulatory impact analysis of $2,892,770,580
(5,084,000 cows slaughtered, at a price of $54.19
per cwt and an average weight of 1,050 pounds)
yields an additional revenue loss on an annual basis
of 0.09 percent.
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importation of up to 160 BSE-infected
cattle into the U.S. (based on APHIS’
estimate for the 95th percentile of
confidence) over 20 years, or the
projected 2 to 20 U.S.-born infected
cattle, should have been considered.
Several commenters expressed concern
that the existence of 21 to 180 cases of
BSE-infected animals could
substantially undercut demand for beef,
as it has done in Europe, or dairy, if the
public begins to identify BSE with the
older dairy breeding stock that are most
at risk of manifesting the disease.
A number of commenters expressed
concern regarding the potential
economic impact of the detection in the
United States of a Canadian-born BSEinfected cow on U.S. export markets.
Commenters stated that the reaction of
the beef markets to the first U.S. case of
BSE—despite that cow’s being of
Canadian origin—demonstrates the very
substantial potential costs to U.S. cattle
industries of introducing even a limited
number of infected animals into the U.S.
herd. Commenters stated that APHIS
should examine such potential
economic impacts.
Response: Expected economic
impacts if new cases of BSE were to
occur in the U.S. cattle population
because of the rule are addressed in the
consequence assessment portion of the
risk assessment we conducted for this
rulemaking. The consequence
assessment notes that effects of BSE
include a variety of costs. Some costs
are long-term; others are one-time costs
uniquely associated with new cases.
The major long-term cost for the
United States due to the diagnosis of
BSE in a cow of Canadian origin in
Washington State in December 2003 has
been reduced access since then to beef
export markets. Principal Asian
markets, in particular, remain largely
restricted. In 2003, the value of U.S.
exports of beef and beef by-products (as
measured by the 33 ‘‘beef only’’ Census
Bureau categories) totaled over $3.9
billion, of which the value of sales to
Asian markets totaled $2.4 billion. In
2004, these totals had fallen to $863
million and $16 million, respectively. In
2006, the value of U.S. beef and beef byproduct exports worldwide was $2.1
billion, and exports to Asia were valued
at $197 million.15
Trade impacts tend to decline over
time as exporting and importing
countries find ways to resume mutually
beneficial trade while maintaining the
safety of the beef supply. The OIE has
developed international science-based
15 Compiled by APHIS using data from the
Department of Commerce, U.S. Census Bureau,
Foreign Trade Statistics.
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animal health standards to permit safe
international trade in beef from
countries that have BSE, based on the
risk level of such countries. The OIE has
classified both the United State and
Canada as controlled risk countries for
BSE.
We anticipate that the economic
impact of any additional cases of BSEinfected cows imported from Canada
will likely be minimal. As noted above,
after the 2003 detection of BSE in
Washington State, many of the 114
nations which imported U.S. beef
banned our beef and live animals, but
over half—including our largest export
market, Japan—have resumed importing
U.S. beef (USDA 2006).16 The joint U.S.Japan press statement for resuming trade
in beef and beef products after market
closures in response to finding BSE in
the United States noted that the United
States has a ‘‘robust’’ food safety system,
and stated that ‘‘identification of a few
additional BSE cases will not result in
market closures and disruption of beef
trade patterns without scientific
foundations’’ (USDA 2004). Adherence
to science is imperative to expanding
trade opportunities and maintaining
existing market access. Continued
import bans by other countries without
sufficient scientific basis to warrant
such measures, and maintained without
adequate assessment of specific risks,
may not be consistent with international
trade obligations, and U.S. Government
agencies continue to work to reopen
such markets.
One of the potential incremental costs
of the detection of BSE in an imported
cow is the regulatory expense of
investigating such cases and paying
indemnity for animals that are
destroyed. Based on the U.S. experience
with native BSE cases that have been
detected, the regulatory costs per case
total approximately $250,000 for
epidemiological investigations and
indemnification of depopulated
animals.
The potential domestic market effects
of any new cases of BSE are difficult to
predict. However, as described in the
consequence assessment in our risk
assessment, there is little reason to
expect that additional U.S. cases of BSE
would have a significant impact on U.S.
beef consumption, based on past
experience.
Although the first U.S. discovery of
BSE, a cow of Canadian origin, resulted
in major restrictions on U.S. beef
exports, that case and subsequent cases
16 The temporary closure of the U.S. export
market to Japan in January 2006 was in response
to a specific commodity concern and not to the
likelihood of BSE infection in the U.S. herd.
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have not, to use the commenter’s term,
‘‘substantially undercut’’ U.S. demand
for beef or dairy products. Studies show
that any negative consumer response to
the discoveries of BSE in Canada and
the United States in May and December
2003, respectively, was neither
significant nor long-lasting.
Consumer opinion surveys as
summarized by Coffey et al. (2005)
indicated that between 14 and 29
percent of respondents reported
reducing their beef consumption.
However, as Kuchler and Tegene (2006)
point out, survey responses may
systematically differ from actual market
behavior. Coffey et al. found that, in the
months following the December 2003
BSE discovery, consumer demand for
beef increased.
Vickner, Bailey, and Dustin (2006)
analyzed weekly grocery store
purchases, from May 9, 2004, to May 1,
2005. The authors studied the impact of
BSE announcements on consumer
demand for beef in Utah over this time
period and found that Utah consumers
were not responsive to BSE
announcements during that period.
Kuchler and Tegene found similar
results on a national scale. The authors
studied three separate markets,
including fresh beef from grocery store
meat counters, frozen beef, and
frankfurters. The study concluded that
the announcement of the finding of BSE
in a Washington State cow may have
reduced purchases of fresh and frozen
beef over a 2-week period, but had no
impact on purchases of frankfurters. A
similar announcement for the finding of
BSE in Canada had no noticeable impact
on beef purchases in the United States.
Although various consumer studies
have concluded that discovery of
additional cases of BSE in the United
States may lead to decreased
consumption of beef, the market has not
substantiated this conclusion. In the
first year after the December 2003 BSE
discovery, beef consumption increased.
While consumption in 2005 was above
1998 levels, consumer demand started
to decline. This decline was likely due
to a combination of factors, including
increased supplies of poultry and a
slowing of growth in consumers’
disposable incomes (Mintert, 2006).
There is no evidence to suggest a
decline in consumption related to the
confirmation of additional cases of BSE
in the United States.
Issue: Several commenters stated that
APHIS’ economic analysis does not
consider potential demand changes
regarding exports of U.S. beef that could
result from implementation of the
proposed rule. A number of commenters
expressed concern that the rulemaking
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would exacerbate the limited access of
U.S. beef to world markets and harm the
ability of the United States to restore
lost export markets. Commenters stated
that imports of Canadian cattle and beef
are currently banned by 35 countries,
including the important U.S. export
markets of the Republic of Korea,
Singapore, and Taiwan, and that APHIS
should not consider relaxing its BSE
import restrictions in light of ongoing
international concerns regarding the
safety of Canadian beef and cattle. Other
commenters stated that the United
States should allow imports only of
classes of cattle and beef that U.S.
export markets are willing to accept
from the United States.
Several commenters expressed
concern that, should Mexico cease
accepting imports of cattle and beef
from Canada, the commingling of
Canadian and U.S. cattle and beef
products would negatively affect the
reopening of Mexico to U.S. live
breeding cattle and the present export of
processed beef to Mexico.
Response: The commenters raise the
concern that, by allowing Canadian
cattle born on or after March 1, 1999, to
be imported into the United States, U.S.
beef export markets will become more
restrictive. Various countries have
enacted different levels of restriction on
beef imports from the United States and
Canada. However, we expect any
restrictions placed on beef from the
United States and Canada by an
importing country to become more
uniform, as discussed below, and,
therefore, for the rule to have little effect
on U.S. beef export markets.
The reason for the expected
uniformity is the May 2007 OIE decision
to classify both Canada and the United
States as BSE controlled risk countries.
By this decision, the OIE recognized the
effectiveness of the science-based
mitigations and interlocking safeguards
in both countries. This classification is
expected to help the beef industries in
both the United States and Canada to
expand their access to export markets.
Issue: One commenter stated that
APHIS’ economic analysis does not
truly analyze the potential ‘‘consumer
welfare’’ of the rulemaking. The
commenter stated that the closest the
analysis gets to considering the
consumer is its consideration of
wholesale buyers of processing beef and
fed beef—whom the commenter stated
APHIS should identify as the primary
beneficiary of the rule.
Response: The principal model that
we use to estimate welfare effects
resulting from the rule does not extend
beyond the wholesale level to retailers
and end buyers of beef. We
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acknowledge this modeling choice in
our discussion of sector impacts in the
analysis for the final rule, and note that
benefits received at the wholesale level
can be expected to be at least partly
distributed downstream to retailers and
final buyers, depending on the levels of
competition. Nevertheless APHIS
believes this modeling choice is
consistent with standard RIA practices,
as recommended by OMB Circular A–4,
and that it adequately identifies the
impact of this regulatory action.
APHIS agrees, however, that some
indication of the distribution of benefits
in different product markets would be
an interesting addition to the model. As
part of the economic analysis for the
final rule, we simulate substitution
among livestock products in response to
relative price changes using a multisector model. Although meant simply to
be illustrative and subject to
considerable uncertainty, included in
the simulations is a derivation of
consumer welfare changes at the retail
level. Results of this analysis suggest
that consumer surplus for buyers of beef
at the retail level may increase by 1.0 to
1.3 percent compared to a 2006
baseline.
Issue: One commenter stated that
APHIS should also broaden the model
used in the economic analysis to
account for cull animal producers, so
that welfare implications to producers
of U.S. cull animals and processing beef
could be separated from those of the
packers. The commenter stated that
APHIS’ analysis includes no single
estimate of the economic impact of the
rule on cow-calf producers resulting
from the change in value and demand
for U.S. cattle.
A number of cow-calf producers
provided estimates of the potential
economic impact of the proposed rule
on their individual operations.
Response: In our regulatory flexibility
analysis for this final rule, we present a
sector-based analysis that includes a
separate consideration of impacts of the
rule for the cow-calf and dairy sector.
The sector analysis uses the measures of
welfare change estimated for cull cattle/
processing beef, feeder cattle, fed cattle,
and fed beef, distributing these changes
among the commodities’ principal
buyers and sellers.
Concerning the numerous comments
we received regarding economic
impacts of the rule on individual
livestock producers, we acknowledge
that analysis does not fully identify the
distribution of all of the possible effects
on the vast array of different types of
entities that comprise the cattle and beef
industries. Because of the different
choices made by market participants, it
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would be difficult, if not impossible, to
design such an analysis. For example,
some large firms likely also act as
wholesalers and distributors, and may
be participants in fed cattle, feeder
cattle, and other markets. The analysis
APHIS has produced does identify the
direct impacts of the regulation on the
industry; the results of our analysis are
based on baseline quantities and prices
and import projections that are well
supported by historical trends and
economic research. The models that we
use to estimate price and welfare effects
are also well-grounded in theory and
utilize methodologies widely accepted
by economists. We are confident that
the results of the analysis appropriately
depict expected net effects of the rule
for the modeled commodities.
Issue: Commenters noted that APHIS
estimated that 46,800 Canadian dairy
breeding animals could be imported
annually into the United States as a
result of this rulemaking. The
commenters expressed concern that
these animals would have a negative
impact on the effectiveness of the
Cooperatives Working Together (CWT)
herd retirement program, which the
commenters noted is funded by
voluntary dairy producer assessments.
(CWT is a national program, organized
by dairy farmers, with the goal of
reducing milk supply and demand
imbalances and, in doing so, of
delivering a significant return on
farmers’ investments through higher,
more stable, milk prices.)
The commenters stated that the
proposed rule would have the effect of
having U.S. dairy farmers assessed to
reduce the U.S. dairy cattle herd, while,
at the same time, cattle are being
imported from Canada to replace those
animals.
One commenter stated that APHIS
should have made the effort to
incorporate ‘‘expected future net
returns,’’ as well as impacts on milk
prices, into an analysis of breeding
cattle imports, and that the economic
analysis should have modeled impacts
on the milk market, and resulting
impacts on producer incomes and the
price of milk cows. Commenters
expressed the opinion that APHIS failed
to meet its obligations under Executive
Order 12866 and the Regulatory
Flexibility Act in its economic analysis
by not performing the required analyses
regarding imported dairy replacement
animals.
Response: We do not expect imports
of dairy animals from Canada to add
significantly to the U.S. national herd,
but, rather, to serve as an additional
source of replacement animals. Dairy
breeding cattle replacements imported
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from Canada during 1992 to 2002
represented about 1.1 percent of U.S.
dairy heifer replacements over this
period. We have no reason to expect the
supply of Canadian heifer replacements
to be greater than historical levels. In
fact, the numbers of dairy heifer
replacements present on all cattle
operations in Canada have been in
decline in recent years, from 512,000 on
January 1, 2003, to 476,300 on January
1, 2007. The number of operations that
specialize in raising heifers has also
decreased. In Ontario and Quebec, there
were 487 of these operations on January
1, 2003, and only 296 on January 1,
2005.17 The currency exchange rate is
also less favorable to Canadian exports
than it was prior to 2003.
There is no evidence that imports of
dairy cattle from Canada have
historically had any significant effect on
the U.S. cow herd, U.S. dairy heifer
prices, or U.S. milk prices. The U.S.
milk herd declined from about 9.7
million head in 1992 to about 9.1
million in 2002. The number of U.S.
milk cow replacements 18 remained
essentially steady, fluctuating between 4
million and 4.1 million head over that
same time period.19 An empirical
investigation by Mussell, et al. (2006) 20
concluded that imports from Canada
prior to 2003 had no statistically
significant impact on the U.S. dairy
herd. Imports of dairy heifers from
Canada were also found to have no
statistically significant impact on U.S.
heifer prices in the United States, nor on
U.S. milk prices.
As noted by commenters, a producer
dairy herd retirement initiative called
CWT is currently underway.21 The
number of imported dairy breeding
cattle projected in our economic
analysis for the proposed rule was based
on historical import levels prior to
formation of CWT. Imports of dairy
heifers are driven by the demand for
replacement animals, relative prices,
and the exchange rate. If dairy farmers
are dedicated to reducing the national
17 Ontario and Quebec account for approximately
two-thirds of the dairy cattle inventory in Canada.
Source: Statistics Canada, as cited in Al Mussell,
Graeme Hedley, Don Ault, and David Bullock,
‘‘Role and Impact of Renewed Canada—U.S. Trade
in Dairy Heifers and Dairy Breeding Stock,’’ George
Morris Centre, Informa Economics, February 2006.
https://www.informaecon.com/
18 Heifers 500 pounds and over kept for milk cow
replacements. Source: Agricultural Statistics,
National Agricultural Statistics Service, USDA.
19 In table 17 of the preliminary Regulatory
Impact Analysis that accompanied our January 2007
proposed rule (Docket No. APHIS 2006–0041),
under column ‘‘Average Annual U.S. Heifer
Replacements’’ the numbers for Beef and Dairy
were transposed.
20 Mussell, et al. (February 2006).
21 https://www.cwt.coop
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dairy herd, they may purchase fewer
replacement animals and the import
projections may be overstated. However,
if a replacement dairy heifer from
Canada can be purchased at a lower
price than a domestic one, then it is to
the producer’s (and industry’s)
advantage for the Canadian replacement
to be purchased and a domestically
raised animal to be retired. Therefore,
APHIS disagrees with the commenters’
claims that dairy producers will
somehow be worse off with this
rulemaking. As a lower priced
replacement heifer would represent a
lower priced input into the production
of dairy products, standard economic
theory indicates that producers and
consumers will be better off.
Issue: One commenter stated that
APHIS’ economic analysis indicates that
imports of dairy cattle from Canada
would be expected to represent ‘‘only’’
1.1 percent of the annual U.S. dairy
heifer crop. The commenter stated that,
although APHIS labels this percentage
as small, a short-term change in the
milking herd of 1 percent can change
milk prices by 10 percent or more.
Response: We agree that a 1 percent
increase in the national dairy herd (and
a corresponding increase in milk
production) may result in a decline in
milk prices. However, as we discuss
above, imports of dairy animals from
Canada that occur should serve as an
additional source of replacement
animals, rather than adding entirely to
the national milking herd. First, we
would reiterate that imports are
voluntary; we believe any projected
imports of dairy heifers would be
undertaken because the cost saving
associated with the import would be
greater than any decrease in revenue
due to relative price declines resulting
from higher production and lower
prices. We further note that we believe
the comment overestimated the
expected price declines due to this
regulatory change. The projected
number of imported dairy cattle is
equivalent to 1 percent of the dairy
heifer crop and not 1 percent of the
entire milking herd, which is more than
twice the size of the annual dairy heifer
crop. Projected imports of dairy heifer
replacements and other breeding cattle
represent approximately 0.45 percent of
the milking herd.
In 2006, the farm-milk supply
produced from 9.1 million dairy cows
was 181.8 billion pounds of milk
(19,951 pounds per cow) at an all-milk
price of $12.90 per cwt, which is a
weighted average of the fluid grade milk
price of $12.92 per cwt and the
manufacturing grade milk price of
$12.21 per cwt. An increase in the size
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of the milking herd would increase milk
production.
If all 47,800 22 dairy heifers projected
to be imported from Canada were to
constitute an addition to the U.S.
milking herd, they would represent a
0.5 percent increase over the 2006 U.S.
herd size. This increase would
correspond to a change in milk
production of approximately 0.5
percent.23 We would expect the shortrun effects (more inelastic supply) of
such an increase in the U.S. milking
herd to be larger than the longer term
effects (more elastic supply). Assuming
a short-run supply elasticity of milk of
0.15 and a demand elasticity of ¥0.30,24
a 0.5 percent increase in milk
production is estimated to decrease the
milk price by 15 cents per cwt. This
translates into a 1.2 percent price
decline. As supply becomes more
elastic, the price decline resulting from
a 0.5 percent increase in production
becomes smaller. Assuming a longer run
supply elasticity of 0.50 would lead to
an estimated decline in price of 9 cents
per cwt, or 0.7 percent.
This example of potential effects on
milk prices due to changes in the size
of the U.S. milking herd assumes that
the projected imports of Canadian
breeding cattle would be absorbed into
the U.S. milking herd in their entirety,
thereby slightly expanding the overall
size of the U.S. milking herd. An
analysis of scenario 3 as discussed in
our economic analysis and in the
summary of that analysis in this
document (entry of Canadian cattle born
on or after March 1, 1999, and
resumption of imports of beef from
Canadian cattle slaughtered at 30
months of age or older) using the multisector model indicates that dairy
producers may experience price
declines of 1.3 to 1.7 percent for dairy
cattle, due to the small number
projected to be imported from Canada.
These imports translate into an increase
in U.S. milk production of 0.1 percent
or less, and a decline in the price of
milk and increase in consumer surplus
of less than 0.1 percent.
22 Projected
annual imports 2008–2012.
the additional heifers produce milk
at the same average rate reported for the U.S. herd
in 2006.
24 Milk supply elasticities of 0.12 in year 1 and
2.46 in year 10 are cited in Chavas, J.P., and R.M
Klemme, ‘‘Aggregate Milk Supply Response and
Investment Behavior on U.S. Dairy Farms,’’
American Journal of Agricultural Economics 78
(February 1986). A total dairy product demand
elasticity of ¥0.31 is cited in Haidacher, R.C., J.R.
Blaylock, and L.H. Meyers. ‘‘Consumer Demand for
Dairy Products, A Summary Analysis.’’ USDA
Economic Research Service, Agriculture
Information Bulletin 537 (March 1988).
23 Assuming
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Issue: One commenter noted that the
importation of live animals from Canada
has enabled many U.S. plants to better
utilize their slaughter capacity, allowing
them to maximize plant efficiencies.
The commenter stated that allowing the
resumption of imports of older animals
to the United States, as envisaged in the
proposed rule, might enable some
previously closed plants to reopen.
Response: The resumption of cull
cattle imports from Canada will provide
increased throughput for U.S. slaughter
plants, especially those that principally
slaughter and process cull animals.
While the cattle from Canada will
enable these businesses to more fully
utilize their available capacities, we do
not anticipate the effects to be highly
significant. Nor are we aware of plants
that have closed and will be reopened
due to reestablished cull cattle imports.
Our analysis for scenario 3 as discussed
in our economic analysis and in the
summary of that analysis in this
document (entry of Canadian cattle born
on or after March 1, 1999, and
resumption of imports of beef from
Canadian cattle slaughtered at 30
months of age or older) indicates that
the additional numbers of cull cattle
marketed over the 5 years, 2008–2012,
will not increase substantially.
Compared to projected U.S. baseline
slaughter numbers averaging 5.4 million
head of cows and 570,000 head of bulls
and stags over the 5-year period,
imports of Canadian cows and bulls/
stags are projected to average 89,400
head and 16,600 head over the same
period, representing 1.7 percent and 2.9
percent of the baseline quantities. These
percentages in fact overstate the
expected impact of the rule in terms of
cull cattle slaughter because they do not
take into account the effect of expected
price declines on domestic sales.
Notwithstanding this cautious
assessment of the extent to which the
rule will benefit U.S. facilities, the
slaughter industry is expected to benefit
from improved operating efficiencies.
Issue: One commenter stated that
APHIS’ economic analysis for the
proposed rule did not consider the
economic implications of the
combination of the rule and Canada’s
implementation of its expanded feed
ban on July 12, 2007, which bans the
inclusion of SRMs in any animal feeds,
pet foods, and fertilizers. The
commenter stated that, under the
expanded Canadian feed ban, SRMs in
Canada will have little or no economic
value. Instead, said the commenter, the
materials will generate a disposal cost,
thereby providing increased incentive
for Canadian producers to ‘‘send all
their cattle over 30 months of age to the
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U.S. for slaughter where the SRMs can
continue to be used as ingredients in
other U.S. animal feed, pet food, and
fertilizer * * *. The result would be an
even greater supply of imported
Canadian cattle than what APHIS
presently predicts and a
correspondingly greater decline in U.S.
cattle prices.’’
Response: We acknowledge that
Canada’s July 2007 expansion of its feed
ban eliminates the value of SRMs for
producers of cattle slaughtered in
Canada, and we agree that the continued
use of SRMs in the United States for
rendered purposes other than as a
component of ruminant feed will
contribute to a difference in prices paid
for cattle at slaughter in Canada and the
United States. Because SRMs are
defined more broadly for cattle 30
months of age or older than for animals
under 30 months of age, this effect on
relative prices in the two countries will
be more notable for cull cattle. For all
cattle, the tonsils and distal ileum are
considered SRMs, whereas for cattle 30
months of age or older, SRMs also
include the brain, skull, eyes, trigeminal
ganglia, spinal cord, vertebral column
(excluding the vertebrae of the tail, the
transverse processes of the thoracic and
lumbar vertebrae, and the wings of the
sacrum), and dorsal root ganglia.
However, even for cull cattle, the
value of rendered SRMs is relatively
minor in comparison to the total value
of the slaughtered animal. In a 2005
analysis of economic impacts of
alternative FDA animal feed regulations,
the value of SRMs was estimated using
a 4-year average of byproduct market
prices.25 For cattle slaughtered at greater
than 30 months of age, the value of
SRMs used in MBM products was
valued at $2.35 per animal, and the
value of SRMs used for tallow was
valued at $2.19 per animal. Thus, the
total value of SRMs from cull cattle used
as rendered byproducts is estimated to
be less than $5 per animal. Given a
projected 2008 nominal value of about
$569 per cow, the income from SRMs
gained by selling the animal in the
United States rather than in Canada will
represent less than 1 percent of the
projected price of the animal at
slaughter.26 Canada’s July 2007 feed ban
25 ‘‘Economic Impacts of Alternative Changes to
the FDA Regulation of Animal Feeds to Address the
Risk of Bovine Spongiform Encephalopathy: Final
Report.’’ Submitted by Eastern Research Group, Inc.
to the Office of Policy and Planning, Food and Drug
Administration, July 25, 2005.
26 Boning utility cow, Sioux Falls, price of $54.19
per cwt, multiplied by an average weight of 1,050
pounds yields an average value of $569 per animal.
Assuming a total value per cow for rendered SRMs
of five dollars: $5/$569 = 0.0088.
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may make the U.S. market more
attractive, but not appreciably.
Issue: One commenter stated that
APHIS’ analysis of the projected
economic effects of the rule should be
revised to take into account the
handling of increased amounts of SRMs.
Response: In the regulatory impact
analysis we conducted for this rule,
projected prices for processing beef and
fed beef incorporate animal slaughter
and meat packing costs, including costs
of handling SRMs. Costs and returns per
animal of handling SRMs are not
expected to change for slaughtering
facilities because of the rule and
therefore do not require specific
analysis. Copies of the full amended
analysis may be viewed on the APHIS
Web site (https://www.aphis.usda.gov/
newsroom/hot_issues/bse/index.shtml),
or be obtained by contacting the person
listed under FOR FURTHER INFORMATION
CONTACT.
Environmental Assessment for the
Rulemaking
Consistent with the National
Environmental Policy Act of 1969
(NEPA), as amended (42 U.S.C. 4321 et
seq.), regulations of the Council on
Environmental Quality (CEQ) for
implementing the procedural provisions
of NEPA (40 CFR parts 1500–1508), and
APHIS’ NEPA implementing procedures
(7 CFR part 372), we prepared an
environmental assessment (EA)
regarding the potential impact on the
quality of the human environment due
to the importation of live bovines and
products derived from bovines under
the conditions specified in our proposed
rule. We made the EA available to the
public and accepted public comment on
its provisions. We discuss below the
issues raised by commenters who
addressed the EA.
Issue: One commenter stated that the
EA that APHIS conducted for the
proposed rule did not adequately
discuss the impact of air emissions from
additional truck round-trips entering the
United States that would result from
importation of cattle 30 months of age
and older from Canada. The commenter
stated that USDA apparently did not
consider the fact that these emissions
would be concentrated in relatively
small parts of the country. Further, said
the commenter, the EA’s discussion of
air pollutants and mitigation measures
is limited to those pollutants regulated
under the Clean Air Act and does not
recognize what the commenter
described as substantial emissions of
greenhouse gases that could result from
the additional truck trips.
Response: Our EA estimated that the
number of additional cattle that would
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be available for importation into the
United States as a result of this rule
would result in a 0.05–0.16 percent
increase in truck transports, compared
to the annual truck transport baseline,
discussed below. However, more recent
data from ERS indicate that the number
of additional cattle that would be
available and eligible for import from
Canada as a result of this rulemaking
initially will be less than the number we
used in the calculations for our October
2006 EA. Consequently, the estimated
number of truck transports initially will
also be less, as will the emissions
generated by such transports.
In the finding of no significant impact
(FONSI) (APHIS 2005a) that APHIS
made in conjunction with our January
2005 final rule, we discussed truck
transports for cattle under 30 months of
age. Prior to implementation of that
final rule, the projected number of
imports of cattle under 30 months of age
would have caused the resumption of
about 35,000 truck transports. The
FONSI for our January 2005 final rule
determined that the result of
environmental impacts from resuming
35,000 trucks transports would be de
minimus. Afterward, based on a
decrease in the projected number of
available imported animals under 30
months of age, the estimated number of
truck transports projected to be resumed
was adjusted downward to range
between 19,460 to 22,140 annually.
As discussed in the EA for this final
rule, for cattle born on or after March 1,
1999, cattle import numbers are
projected to range between 130,000 to
446,000 over a 20-year period after
implementation of this rule. The
number of associated truck transports
that would resume for this rule would
range from 2,600 to 8,920. When added
to the truck transports resumed as a
result of our January 2005 final rule, the
total number of projected resumed truck
transports is still within the amount
described in the FONSI for our January
2005 final rule as de minimus.
Additionally, that projected number is
within the number of truck transports
for cattle trade that occurred between
Canada and the United States before
such trade was temporarily halted in
May 2003.
As we stated in our EA, the transport
of cattle could occur through any of 20
U.S.-Canadian border ports specifically
equipped to handle cattle. These ports
are not confined to one region of the
United States, but stretch across nine
northern border States from Washington
to Vermont. Market patterns and
geographic issues can cause fluctuations
in the availability and importation of
cattle. Availability of cattle for
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importation also can vary depending
upon the time of year and geographic
location. For example, most feeder cattle
are imported through certain western
ports from areas with the highest cattle
population in Canada, and more feeder
cattle may become available in the fall
when ranchers wean calves and sell
them. Cull cattle for immediate
slaughter historically have come
through different ports than feeder
cattle, including some eastern ports.
Emissions from trucks importing cattle
from Canada could affect any of the 20
locations at the U.S.-Canadian border
and any location between transport
origination and destination.
In determining if the impacts from
truck transport emissions from carrying
additional cattle as a result of this rule
could result in a significant impact on
the environment, a baseline of the
annual overall truck transports was
used. In this case, the baseline used for
comparison was for all incoming trucks
from Canada to the United States
through 20 approved ports of entry
where cattle can transit to determine
whether the increase in the numbers of
imported cattle would cause a
significant increase in air emissions.
The comparison of the baseline (the
average number of heavy-duty truck
crossings annually between the U.S.Canadian border) to the number of truck
transports estimated for cattle 30
months of age and older that would be
available to be imported from Canada
annually shows that the increase in the
number of truck transports would not be
significant.
To a great extent, projecting the
specific air emissions that would result
from implementation of this rule would
be speculative. Emissions vary
according to many different factors,
including type of truck engine, the year
the engine was manufactured, fuel
properties, the type of hauler and
weight of the load, the grade of the
highways on the transport routes, the
distance traveled, speed and
acceleration, and the amount of wait
time at the border ports. Due to the
comparatively small amount of truck
transports (ranging from 2,600 to 8,920)
that are projected to result from this rule
in relation to the baseline, speculating
on the specific air emissions that would
result from this rule would not result in
information indicating that the indirect
impacts, unassociated with the scope of
this rule, would contribute to significant
adverse impacts on the environment
from resuming imports from Canada of
cattle over 30 months of age born on or
after March 1, 1999.
The method of transporting cattle and
the type of vehicle to be used are not
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mandated by APHIS regulations.
Emissions from the transport of cattle,
or of any commodity moved by modern
transport methods, are unavoidable.
However, measures to reduce the
impacts from vehicle emissions are
enforced by environmental statutes,
such as the Clean Air Act, at both the
State and Federal levels and have been
reported to be effective in regulating and
decreasing vehicle emissions.
Mitigations for vehicle emissions are
under the jurisdiction of the U.S.
Environmental Protection Agency and
State government agencies and are
outside of the mission of APHIS.
The commenter is correct that the EA
did not discuss the contribution of
greenhouse gases from the transport
trucks that would be used to import
cattle and did not discuss mitigation
measures for greenhouse gases. We note
that draft guidance provided to Federal
agencies from the Council on
Environmental Quality with regard to
consideration of global climatic change
in environmental documents calls for
consideration, in the context of NEPA,
of how major Federal actions could
influence the emissions and sinks of
greenhouse gases and how climate
change could potentially influence such
actions.27 We interpret that this
guidance does not apply to this
rulemaking because it is not a major
Federal action that could influence the
emissions and sinks of greenhouse
gases .28
Issue: One commenter stated that
APHIS’ EA did not assess the
environmental impact of holding and
feeding in the United States each year
hundreds of thousands of Canadian
cattle 30 months of age or older.
Response: Approximately 34 million
head of cattle are slaughtered in the
United States each year. Approximately
0.13 to 0.45 million additional head of
cattle would be available annually and
eligible for importation from Canada
under this rulemaking. The majority of
cattle that we anticipate being imported
from Canada and held in feedlots will
be cattle under 30 months of age that are
already allowed importation from
Canada under our January 2005 final
27 Memorandum to All Federal NEPA Liaisons,
dated October 8, 1997, from Dinah Bear, General
Counsel, Executive Office of the President, Council
on Environmental Quality, with attached draft
memorandum from Kathleen A. McGinty,
Chairman, on Guidance Regarding Consideration of
Global Climatic Change in Environmental
Documents Prepared Pursuant to the National
Environmental Policy Act.
28 A sink is, simply speaking, the converse of a
source. Instead of releasing carbon into the
atmosphere as is done when fossil fuels or wood are
burned, sinks absorb carbon and lock it in. The
most obvious examples are trees and other plants.
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rule. The majority of additional cattle
that we expect to be imported as a result
of this rulemaking would consist of
cows, bulls, and stags imported directly
for slaughter that would remain in a
holding facility of the slaughter facilities
for approximately 1 to 2 days before
slaughter. A small percentage of the
remainder of the cattle that we expect to
be imported as a result of this
rulemaking would consist of breeding
cattle (for example, dairy or beef cows
and heifers and bulls) that would be
integrated into a cattle herd for an
indefinite period of time. Thus, for
purposes of the EA, the cattle that
would be imported would not be held
in feedlots for a long duration and
would not contribute to an increase to
the baseline of the number of cattle
produced in the United States and held
and fed in feedlots each year.
Pollutant discharges and emissions
from holding cattle in feedlots are
unavoidable; however, measures to
reduce the impacts from feedlot
discharges and emissions are enforced
by environmental statutes, such as the
Clean Water Act and the Clean Air Act,
at both the State and Federal levels.
Requirements for mitigating pollutant
discharges and emissions, under the
jurisdiction of Federal and State
government agencies, are intended to
protect the human environment of the
United States.
Issue: One commenter expressed the
opinion that our EA was inadequate
because, according to the commenter, it
failed to explain why the potential for
widespread distribution of infectious
BSE prion proteins is not a significant
environmental impact. The commenter
expressed concern that blood and SRMs
that will be collected when cattle of
Canadian origin that are over 30 months
of age are slaughtered can be used as
fertilizer and be spread on the ground
(and ingested as well as running off into
streams) on farms throughout the United
States. The commenter stated further
that the EA did not assess the
environmental impact of distributing
infectious BSE prion proteins in animal
feed that will be used (and spilled,
disposed of, and excreted) on farms
across the United States. The
commenter stated that OIE guidelines
prohibit trade in SRMs for use in
fertilizer, as well as trade in fertilizer
contaminated with SRMs.
Response: The commenter did not
specify, and it is not clear to us, in what
manner the commenter anticipates
prions being widely distributed through
animal feed and fertilizer and having a
significant impact on the quality of the
human environment. Scientists believe
that the primary route of BSE
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transmission in cattle requires that an
animal ingest feed that has been
contaminated with a sufficient amount
of tissue from an infected animal. In
humans, vCJD, a chronic and fatal
neurodegenerative disease of humans,
has been linked via scientific and
epidemiological studies to exposure to
the BSE agent, most likely through
consumption of cattle products
contaminated with the BSE agent.
Therefore, our assumption is that the
commenter’s primary concern regarding
the potential impact of feed and
fertilizer on the environment is the
potential consumption of BSEcontaminated feed or fertilizer by
ruminants or humans. We also consider
it possible that the commenter is
concerned about the potential for the
BSE agent to be consumed by animals
other than ruminants, excreted by those
animals, and subsequently consumed by
ruminants or humans.
The commenter stated that APHIS
inadequately assessed the potential
environmental impact of contaminated
feed and fertilizer. We disagree with the
commenter. Our EA evaluated the
potential impact of the proposed rule on
the physical environment, public
health, and endangered species, as well
as cumulative impacts of any of the
above. The EA referenced and discussed
the conclusions of the risk assessment
we conducted for this rulemaking, in
which we assessed the likelihood that
U.S. cattle would be exposed to the BSE
agent as a result of this rule. Our risk
assessment examined the likelihood of
exposure of ruminants to BSE via feed.
Our evaluation of risk included an
understanding that SRMs from live
cattle imported under the conditions of
the proposed rule would enter the U.S.
rendering system, in the same fashion
that SRMs from cattle of U.S. origin are
generally disposed of. The protein
products from the rendering system
could then be incorporated into either
animal feed or fertilizer. We assumed in
the risk assessment that the vast
majority of rendered protein products
are sold for use in animal feed. The
commenter makes this assumption as
well, stating that ‘‘* * * SRMs can be
used as a protein source for animal feed
other than ruminant feed, and it is
reasonable to assume that they will be,
given the favorable economics of this
use as compared to SRM disposal.’’
The quantitative exposure model used
in the risk assessment specifically
simulated potential exposures through
feed—either through ruminant feed that
was mislabeled or cross-contaminated,
through other animal feed that was
misfed to ruminants, or directly through
poultry litter that could contain spilled
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feed and be fed back to cattle. These
pathways are the most direct exposure
of cattle that could occur.
We disagree with the commenter’s
assertion that APHIS did not consider
‘‘spilled, disposed of, or excreted’’
animal feed as a potential pathway of
BSE transmission. The poultry litter
pathway modeled in the quantitative
exposure model specifically addresses
spilled and even undigested excreted
feed, with very conservative
assumptions about potential infectivity
retained in such feed. The issue of feed
being ‘‘disposed of’’ is addressed
through the misfeeding component of
the model, which incorporates
situations where non-ruminant feed is
fed directly to cattle. These situations
would include those where a producer
either mistakenly or intentionally feeds
non-ruminant feed to ruminants.
Mislabeling and misfeeding components
would include situations where nonruminant feed is sold for salvage value.
We are not aware of similar situations
where litter or waste from other
species—for example, swine litter—that
contains quantities of either spilled or
undigested feed is routinely used for
cattle feed. Further, there is no evidence
to date of environmental contamination
(e.g., via fecal or other bodily
excretions) being a route of transmission
of BSE. Therefore, we do not consider
there to be potentially significant
pathways for exposure of susceptible
animals to BSE-contaminated feed that
were not considered in the risk
assessment.
With regard to potential exposure of
humans to the BSE agent, there is no
evidence, anecdotal or otherwise, to
suggest any likelihood of BSEcontaminated animal feed, spilled or
excreted, being consumed by humans,
and we consider the risk of such
exposure to be negligible.
The commenter also stated that the
EA should have examined the potential
impact on the environment of BSEcontaminated fertilizer. As noted above,
although rendered protein can be a
component of fertilizer, such usage is
not common because most rendered
proteins are sold for use in feed. Any
consideration of animal health exposure
from fertilizer would be an evaluation of
the risk of cattle exposure to BSE
through oral consumption of fertilizer
that contains rendered protein. Our
quantitative exposure model evaluates
the potential oral exposure of cattle to
feed containing such rendered protein.
It does not specifically model potential
exposure through fertilizer. However, it
assumes that all rendered ruminant
protein products are sold for feed use.
Therefore, any of the infectivity
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contained in rendered ruminant protein
is already simulated through the
potential for direct feed exposure. This
is a more direct pathway than any
potential consumption of a component
of a fertilizer product, some undefined
time after it was spread on a pasture.
Therefore, any potential exposure
through fertilizer would be assumed to
be far less than the exposure the model
already takes into account through the
consumption of feed.
It appears that the commenter is
suggesting that raw, untreated SRMs
might be spread directly on land as
fertilizer. Raw or untreated tissues are
not generally used as fertilizer, and, in
fact, are often prohibited from being
spread on land through environmental
regulations on carcass/offal disposal and
solid waste disposal. Therefore, this risk
pathway was not considered in our risk
assessment.
With regard to the likelihood of
exposure of humans to the BSE agent
through fertilizer, we are assuming the
commenter is not referring to potential
consumption by humans of fertilizer,
and is referring instead to some other
method of BSE transmission to humans
through fertilizer. As noted above, there
is no evidence to date of environmental
contamination being a route of
transmission of BSE.
Regarding the commenter’s statement
that OIE guidelines recommend that
trade not be carried out in SRMs for use
in fertilizer, as well as trade in fertilizer
contaminated with SRMs, the primary
purpose of such guidelines is to reduce
the possibility of the consumption by
cattle of such product due to
mislabeling or misdirection of
shipments—e.g., through having SRMderived protein for fertilizer mistakenly
sent to a feed mill.
Other Issues
A number of commenters raised other
issues that did not address the
provisions of the proposed rule.
Requests Regarding the Importation of
Additional Commodities
We received comments that requested
that bovine commodities not
specifically addressed in our proposed
rule be made eligible for importation
into the United States.
Issue: Several commenters requested
that U.S. regulations with regard to BSE
allow the importation of the same
commodities that Canada considers
eligible for importation from the United
States.
Response: Although in most cases,
Canadian and U.S. import restrictions
regarding BSE are comparable, we do
not consider it practical or advisable to
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attempt to mirror the regulations of
another country, given differences in
regulatory approach, structure, and
authority.
Issue: Commenters requested that the
current regulations be amended to allow
the importation from BSE minimal-risk
regions of rendered feed products—
including bovine-derived meat-andbone meal and blood meal—that are
manufactured in compliance with U.S.
regulations if the products can be
determined to meet the health
protection objectives of the
recommended standards of the OIE.
Response: The recommended
standards of the OIE clearly state that
ruminant-derived rendered protein
should not be traded from either
controlled risk or undetermined risk
countries.
For the reasons discussed above, we
are making no changes based on these
comments.
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APHIS’s Use of the Term ‘‘Minimal-Risk
Region’’
Issue: Several commenters requested
that APHIS discontinue classifying and
referring to countries as ‘‘BSE minimalrisk regions.’’ The commenters stated
that APHIS’s definition of ‘‘minimal-risk
regions’’ does not follow the scientific
terminology of the OIE, which classifies
countries with regard to BSE risk as
‘‘negligible,’’ ‘‘controlled,’’ or
‘‘undetermined.’’ One commenter stated
that APHIS’s classification of BSE
minimal-risk regions may create
confusion and be seen as not accepting
the OIE categorization criteria.
Response: At the time APHIS
published its January 2005 final rule to
recognize a category of BSE minimalrisk regions, the OIE guidelines
regarding BSE provided for five possible
BSE classifications for regions. For each
classification, the guidelines
recommended different export
conditions for live animals and
products, based on the risk presented by
the region. Although APHIS did not
incorporate the text of OIE’s BSE
guidelines into its January 2005 rule, the
agency based its standards regarding
BSE minimal-risk regions on these
guidelines. Although we are making no
changes based on the comments, it is
APHIS’s intent to develop rulemaking
that would more closely employ
terminology used in the current OIE
standards.
BSE Surveillance in the United States
Issue: Several commenters expressed
general concern with the effectiveness
of the current BSE testing program in
the United States. One commenter
stated that a report issued by the U.S.
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Office of the Inspector General (OIG)
called into question USDA’s ability to
adequately detect BSE, even before the
most recent reduction in the U.S.
surveillance program. The commenter
stated that an OIG report pointed to the
voluntary nature of the surveillance
program and the program’s sampling
protocols as indicators that the
surveillance program may not have been
providing an accurate picture of BSE
prevalence in the United States. The
report also noted that the surveillance
program, which focused on high-risk
cows, did not account for emerging
evidence that BSE has been detected in
seemingly healthy animals.
Response: We assume the commenters
are referring to an OIG audit report
issued in August 2004. This audit was
conducted prior to the implementation
of the enhanced surveillance program
and, therefore, was limited in the
conclusions that could be made about
the performance of that effort. The
report stated the following: ‘‘Our review
was limited because implementation
plans have not been finalized and
APHIS has not yet been able to address
some of the questions we have raised.’’
Nevertheless, APHIS responded to the
recommendations provided by OIG and
addressed the issues raised. A second
audit report was issued in January 2006,
covering both the surveillance program
and FSIS’ controls on SRM
requirements and advanced meat
recovery products. This report included
a recommendation, among others, for
transparency in the analysis and
conclusions derived from the data
obtained during the surveillance efforts.
APHIS has subsequently completed and
released a detailed summary of the data
obtained during the enhanced
surveillance effort, and an estimate of
the prevalence of BSE in the United
States adult cattle population. This
analysis concluded that the prevalence
of the disease in this country is
extremely low, less than 1 case per
million adult cattle. Two models were
used to estimate the prevalence, and the
most likely values calculated by these
models for the estimated number of
cases were 4 or 7 infected animals out
of 42 million adult cattle. APHIS’
analysis was submitted to the scrutiny
of a peer review process, and the expert
panel agreed with the appropriateness
of APHIS’ assumptions and the factors
it considered, as well as with the
estimate of BSE prevalence.
Country-of-Origin Labeling
A number of commenters
recommended that APHIS postpone
implementation of this rule until
mandatory country-of-origin labeling, as
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prescribed by the 2002 Farm Bill, is in
place in this country.
Response: On May 13, 2002, President
Bush signed into law the Farm Security
and Rural Investment Act of 2002, more
commonly known as the 2002 Farm Bill.
One of its many initiatives requires
country of origin labeling (COOL) for
beef, lamb, pork, fish, perishable
agricultural commodities and peanuts.
On January 27, 2004, President Bush
signed Public Law 108–199 which
delays the implementation of mandatory
COOL for all covered commodities
except wild and farm-raised fish and
shellfish until September 30, 2006. On
November 10, 2005, President Bush
signed Public Law 109–97, which
delays the implementation for all
covered commodities except wild and
farm-raised and shellfish until
September 30, 2008. As described in the
legislation, program implementation is
the responsibility of USDA’s
Agricultural Marketing Service.
The COOL program, when fully
implemented, will address the concerns
raised by commenters with regard to
APHIS’ proposed rule. APHIS does not
consider it necessary to delay
implementation of this rule until those
labeling provisions are implemented. In
its October 30, 2004 proposal, AMS
noted, in discussing Section 10816 of
Public Law 107–171 (7 U.S.C. 1638–
1638d) regarding COOL that the ‘‘intent
of the law is to provide consumers with
additional information on which to base
their purchasing decisions. It is not a
food safety or animal health measure.
COOL is a retail labeling program and
as such does not address food safety or
animal health concerns.’’
Comments on Other Issues Outside the
Scope of This Rulemaking
A number of other comments also
addressed topics outside the scope of
the proposed rule. These comments
included the following issues: Concern
that the examination and euthanization
of cattle be carried out in a humane
fashion; a request to extend the U.S. ban
on the slaughter of nonambulatory cattle
to include all livestock species;
recommendations regarding the type of
penalties USDA should impose for
noncompliance with the regulations;
comparison of U.S. and Canadian
regulations regarding the rendering of
cattle slaughtered on-farm; the
importation of composted bovine
manure from BSE minimal-risk regions;
a request to allow the importation of
breeding stock and embryos of small
ruminants, such as sheep; a request that
the USDA allow the importation from
BSE minimal-risk regions of up to 5
kilograms of bovine meat and meat
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products for personal use without
certification; and concerns regarding
diseases other than BSE.
For the reasons discussed above, we
are making no changes to the proposed
rule based on these comments.
Final Report From Peer Review of
APHIS’ Risk Assessment and Responses
to Peer Reviewer Questions and
Recommendations
As discussed above under the heading
‘‘Peer Review of APHIS’ Risk
Assessment,’’ we requested an external,
formal, and independent peer review of
our risk assessment by recognized
experts in the field. The objective of the
peer review was to determine whether
the risk assessment was scientifically
sound, transparent, and consistent with
international standards (e.g., those
developed by OIE); the application of
external assessments or models was
appropriate; and the assumptions were
justified, supported and reasonable. In
summary, the reviewers found that the
methods used in the risk assessment
were scientifically rigorous in terms of
using existing literature and models
appropriately and making sound
assumptions and that the risk
assessment itself adhered to
international risk assessment standards.
The reviewers also agreed with the
conclusion that the likelihood of
establishment of BSE in the U.S. cattle
population is negligible. They also
asked a variety of questions and
suggested minor refinements. APHIS’
full response to the comments and
recommendation of the peer reviewers
may be viewed on the APHIS Web site
(https://www.aphis.usda.gov/newsroom/
hot_issues/bse/index.shtml ).
Some of the questions raised by peer
reviewers were also posed in public
comments on our proposed rule and are
addressed above in our responses to
public comments. In addition, we set
forth here certain other questions and
recommendations from peer reviewers
that we consider representative of the
content-related questions and
recommendations of the report, and our
response to those questions and
recommendations.
Issue: A reviewer suggested that we
more explicitly list the specific risks to
be addressed in the assessment.
Response: The risk of BSE evaluated
in the assessment is the expected impact
of importing from Canada live animals,
blood and blood products, and small
intestines excluding distal ileum. These
impacts include the potential for
establishment of BSE in the United
States and the projected consequences
of any additional cases that might occur
even without establishment. The risk
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was evaluated qualitatively for all
commodities and also quantitatively for
additional live animal import scenarios.
For the latter, the likelihood of
establishment is measured by the
disease reproductive rate (R0). We also
simulated the total number of animals
in the United States that might become
infected with BSE as a result of the
importation of live bovines from Canada
over the 20 years. Of the infected
animals, those that we assumed might
have economic impacts were only the
animals expected to live long enough to
display clinical signs, as these are the
most likely to be detectable with current
testing methods. We have added this
clarification to the Introduction of the
revised risk assessment.
Issue: A reviewer suggested that the
analysis needs to acknowledge the
exogenous sources of BSE into Canada.
As phrased by the reviewer:
For the assumption that BSE prevalence in
Canada would decrease over the next 20
years until the disease is eradicated, the
authors relied on compelling evidence from
the U.K. experience with the ruminant feed
ban and the resulting dramatic decrease in
BSE prevalence in cattle. However, this did
not address any issues associated with
exogenous sources of BSE into Canada
(imports from other BSE-affected countries).
The Canadian prevalence model used for this
analysis appears to assume no new
exogenous sources of BSE. The dilution of
risk due to current practices that reduce the
likelihood of spread of prions through the
Canadian cattle herd make this risk minimal
at best, but it should be addressed for the
sake of completeness.
Response: The prevalence estimation
models use BSE surveillance data (test
results from dead or slaughtered cattle)
as inputs and therefore cannot
differentiate whether the source of
infectivity is endogenous (recycled) or
exogenous (introduced). Also, because
they are based on actual surveillance
data, they cannot attempt to predict any
changes in Canadian BSE prevalence
over the next 20 years. The qualitative
prediction of a drop in prevalence is
based on the experience in the United
Kingdom and does not assume that no
additional infectivity can be introduced.
In addition, the results of the U.S.
Harvard model presented in our risk
assessment illustrate that, despite the
recurrent release of ‘‘exogenous
infectivity’’ (in this case, from Canada),
the reproductive constant, R0, remains
well below one, indicating that the
mitigations in place (particularly the
ruminant feed ban) are effective in
driving disease prevalence downward.
Since the feed ban in Canada is very
similar to that in the United States, we
expect that any additional infectivity
that may potentially enter Canada
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would fail to alter our predictions of a
decrease in prevalence over time. For
these reasons, we do not explicitly
address the source of BSE infectivity in
Canada as either endogenous or
exogenous.
Issue: A reviewer suggested that we
address the amount of uncertainty that
is associated with the conclusion that
the likelihood of releasing BSE into the
United States from Canada via
importation of live bovines is extremely
low. He suggested that we report and
use the 95th confidence levels
throughout the assessment.
Response: Uncertainty between
prevalence estimation models (BBC or
BSurvE) is greater than the statistical
uncertainty within prevalence
estimation models (represented by
confidence levels for a given model).
Therefore, uncertainty about prevalence
is addressed by considering the two
expected (average) prevalence estimates
obtained with different models. The
reviewer also commented that the
expectation that prevalence remains
stable at the lower level estimated by
the BBC model over the next 20 years
is ‘‘a very pessimistic assumption.’’
Similarly, another reviewer stated that it
is ‘‘very reasonable’’ to assume that BSE
prevalence in Canada will decrease over
the next 20 years until the disease is
eradicated . If these assertions are
correct, then assuming that prevalence
remains stable at the 95 percent (or 99
percent) confidence level estimated by
the BSurvE model over the next 20 years
would simply result in a more
extremely pessimistic assumption. A
reviewer commented: ‘‘It should’be
pointed out that the other pessimistic
assumptions in the Exposure
Assessment model (for example no
decrease in BSE prevalence over the
next 20 years) would likely override any
underestimate of the present BSE
prevalence due to using the mean BBC
prevalence estimate.’’ For the reasons
noted above, we have elected not to
rerun the exposure model using the 95
(or 99) percent confidence level.
Issue: A reviewer commented that
‘‘[o]ne argument that might be made is
that introduction will not lead to an
establishment of a cycle of infection but
may extend the temporal occurrence of
the number of cases of BSE in the U.S.
Are there any adverse economic effect[s]
associated with this outcome? One
possibility is that testing levels might
need to be maintained for a longer time
than if there were no more introduced
and detected BSE cases. Market access
and prices for beef and beef products
might also be adversely affected.’’
Response: The APHIS risk assessment
did not consider endogenous levels of
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BSE in the U.S. cattle herd; however,
continuous exogenous inputs of BSE
infectivity from Canada (as is assumed
in the less likely quantitative scenarios
of the risk assessment) or any other
source would extend the time to
eradication of the disease in the United
States. Although the incremental
duration of the extended time to
eradication is unknown, we expect that
it would have little or no practical effect
on the potential economic impacts of
BSE in the United States. We note that
the exposure model, which incorporates
several risk-inflating assumptions,
estimates that, over the 20 years of the
analysis, there will be less than one
clinical case of BSE in the United States
as a result of the cattle imported from
Canada. Given that the United States
has already detected three BSE cases
(two in native cattle), we do not expect
any incremental impact (from a
lengthened period of testing or from
additional market impacts) of this very
small number of potential additional
cases. This point is described in detail
in the consequence section of our risk
assessment.
Issue: One reviewer requested greater
attention to uncertainty throughout the
document. The reviewer stated, in
reference to our risk assessment, that
‘‘uncertainty is consistently
underplayed if not ignored’’ and ‘‘it
would perhaps be useful to actually list
the sources of uncertainty in each of the
sections. Another commenter suggested
that we list all the model inputs
considered to be variable.
Response: We disagree with the
reviewers. Though not always addressed
as distinct lists, uncertainty and
varibiality are incorporated throughout
the risk assessment. The models used in
the risk assessment are complex with a
large number of inputs, which, as for
most models, may be somewhat
uncertain and/or variable. However,
preparing a comprehensive list of
uncertain and/or variable risk
assessment model inputs is not
necessary. In our judgment, the inputs
are better discussed in the context of
how they are used in the model.
All of the BSE prevalence estimation
model inputs represent best available
estimates of either a variability
distribution (e.g., BSE incubation
period, cattle age structure) or a
parameter value (e.g., number of adult
animals in the herd, age of a BSE tested
animal). Consequently, the calculated
confidence intervals represent statistical
uncertainty about current BSE
prevalence related to random sampling
error. The major source of uncertainty
regarding BSE prevalence in the current
standing cattle population was
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considered to be the effect of the
Canadian feed ban. This uncertainty
was addressed by considering two BSE
prevalence estimation models: The BBC
model, which incorporates an estimate
of the effect of the feed ban based on
evidence from the United Kingdom, and
the BSurvE Prevalence B model, which
makes no assumptions about the effect
of the feed ban. Variability also entered
into the prevalence calculation in that
the BBC prevalence model assumes that
birth year cohort prevalence declined
during the first five years after Canada
introduced a feed ban in 1997.
Thereafter, both the BBC and BSurvE
models were used to obtain the
expected proportion of BSE infected
animals, which is assumed to remain
constant over time in the quantitative
risk analysis.
Another component of the release
assessment, for which uncertainty has
not been addressed, is the projection of
imports. These projections were
prepared by USDA ERS and were based
on USDA baseline projections and a
broad array of expert opinion. Because
they are projections, they are uncertain.
This uncertainty has been reduced
somewhat by incorporating more recent
data into the 2007 import projections,
prepared for the final rule. Based on
these updates, we expect lower numbers
of older animals to be imported in the
early years of the rule’s implementation.
The total imports over the entire 20
years of the analysis are only slightly
(125,000 animals) higher than the
original and so do not confer significant
additional magnitude of release
(125,000*0.68*10¥6=0.085 cases;
125,000*3.9*10¥6=0.49 cases).
Therefore, although the import
projections are somewhat uncertain,
reduction of this uncertainty has not
significantly changed our release
estimates or conclusions.
The projections used in the original
analysis incorporated temporal
variability across years due to the cattle
cycle. The variability considered did not
include possible but less likely extremes
(shocks), such as a temporary spike in
slaughter rates due to severe weather.
The parameters for the exposure
model have been described in earlier
documents (Cohen, et al., 2003). These
documents explicitly examined the
effects of uncertainty in key parameters
in their respective sensitivity analyses.
The version of the Harvard model
performed for this rule included a
sensitivity analysis to examine the
uncertainty of several parameters—some
of which were included in earlier
models, and some of which were new
parameters (e.g., the amount of chicken
litter incorporated into ruminant feed)
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and the Canadian BSE prevalence
estimate) (APHIS 2007a). Of the
uncertain parameters examined,
Canadian BSE prevalence over the next
20 years was the most significant source
of uncertainty for the model. This
uncertainty contains two components:
The estimate of prevalence in Canada’s
current standing cattle population, and
how prevalence of BSE in Canada will
change over time. This latter component
was not treated quantitatively, and its
uncertainty was therefore not explicitly
analyzed in the sensitivity analysis.
Variability in this parameter was
addressed, however. Assuming constant
prevalence over the next 20 years, the
simulated number of BSE infected cattle
imported each year still varies, because
it is a combination of the predicted
import volume (which varies as
described above), and the sampling
variation (using a Poisson distribution)
about the expected prevalence value.
This source of variation has already
been described in the risk assessment.
In conclusion, rather than perform a
comprehensive uncertainty analysis in
which all model inputs are treated as
statistical distributions, we identified
and evaluated the potential
contributions to variability and
uncertainty that we deemed most
relevant to our analysis. Given that the
uncertainty about the key inputs to the
risk assessment models has been
considered, we agree with the reviewers
that further uncertainty analysis will not
affect the conclusions of the risk
assessment.
Adoption of this Final Rule
Therefore, for the reasons given in the
proposed rule and in this final rule, we
are adopting the proposed rule as a final
rule, without change.
Applicability of the March 1, 1999, Date
to Imports of Beef
Issue: Several commenters stated that
it was not clear from the proposed rule
whether the March 1, 1999, date of birth
requirement for live bovines imported
into the United States from Canada
would apply as well to frozen beef
products derived from cattle slaughtered
in Canada and shipped to the United
States. If the same effective date does
not apply, stated the commenter, USDA
should specify what date would be used
for imported frozen beef products. One
commenter stated that, in addition to
prohibiting the importation of beef from
cows born before March 1, 1999, the
regulations should limit the importation
of beef from BSE minimal-risk regions to
that derived from cows slaughtered no
earlier than March 1, 1999.
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Response: We do not consider it
necessary to address the importation of
beef from BSE minimal-risk regions in
this rulemaking, because the
importation conditions for meat, meat
byproducts, and meat food products
derived from bovines were addressed in
the rulemaking for our January 2005
final rule (in which we added the
category of BSE minimal-risk regions to
the regulations and specified which
commodities may be imported from
such regions). The risk analysis we
conducted for that rulemaking indicated
a low BSE risk from such commodities
derived from bovines of any age if
certain conditions are met. In that
rulemaking, we discussed regulatory
requirements implemented by FSIS in
2004 that banned SRMs from the human
food supply in the United States, and
we stated that the Canadian Government
had established similar safeguards in
Canada.
Consequently, we provided in § 94.19
of the regulations that meat, meat
byproducts, and meat food products
derived from bovines are eligible for
importation from BSE minimal-risk
regions if the following conditions, as
well as all other applicable
requirements of the regulations, are met:
• The commodity is derived from
bovines that have been subject to a
ruminant feed ban equivalent to the
requirements established by the U.S.
Food and Drug Administration at 21
CFR 589.2000;
• The commodity is derived from
bovines for which an air-injected
stunning process was not used at
slaughter; and
• The SRMs and small intestine of the
bovines from which the commodity was
derived were removed at slaughter.
Because there is negligible risk from
bovine meat, meat byproducts, and meat
food products that meet the above
requirements, there is no science-based
reason to require that such commodities
be derived from bovines born on or after
March 1, 1999. As long as the
commodities meet the conditions listed
above (with the exception of the
condition regarding small intestine as
discussed in this rule), the regulations
will allow for their importation into the
United States. We note that the OIE
guidelines for trade in fresh meat and
meat products from cattle from
controlled risk regions (both Canada and
the United States are classified as BSE
controlled risk regions under the OIE
guidelines) recognize the negligible risk
presented by such products as long as
SRMs are removed, and, therefore, the
guidelines do not recommend that the
date of birth of the animal from which
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the commodity was derived be a
condition for such trade.
Comments Regarding the Partial Delay
in Applicability of the January 2005
Final Rule
Issue: As discussed above in this
document, in March 2005, APHIS
published a final rule in the Federal
Register that, pursuant to an
announcement by the Secretary of
Agriculture in February 2005, delayed
the applicability of the provisions in our
January 2005 final rule as they apply to
the importation from Canada of meat,
meat food products, and meat
byproducts (other than liver) when
derived from bovines 30 months of age
or older when slaughtered, as well as
certain other bovine products when
derived from bovines 30 months of age
or older.
A number of commenters either
questioned whether the delay in
applicability would be lifted if our
January 2007 proposed rule were made
final, or requested that the delay be
lifted.
Response: As discussed above, it is
the Secretary’s intent to remove the
delay in applicability when this rule
becomes effective.
Executive Order 12866 and Regulatory
Flexibility Act
This rule has been reviewed under
Executive Order 12866. The rule has
been determined to be economically
significant for the purposes of Executive
Order 12866 and, therefore, has been
reviewed by the Office of Management
and Budget.
We have prepared an economic
analysis for this rule. The economic
analysis provides a cost-benefit analysis
as required by Executive Order 12866
and a final regulatory flexibility analysis
that examines the potential economic
effects on small entities as required by
section 604 of the Regulatory Flexibility
Act. The economic analysis is
summarized below. Copies of the full
analysis may be viewed on the APHIS
Web site (https://www.aphis.usda.gov/
newsroom/hot_issues/bse/index.shtml),
or be obtained by contacting the persons
listed under FOR FURTHER INFORMATION
CONTACT.
This rule will allow the importation,
under certain conditions, of the
following commodities from BSE
minimal-risk regions (currently only
Canada):
• Live bovines that were born on or
after March 1, 1999;
• Bovine small intestines, minus the
distal ileum;
• Bovine casings; and
• Bovine blood and blood products.
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APHIS has determined that the
previous restrictions are not warranted
by scientific research and evidence, and
that they are unnecessary for
maintaining a negligible risk (i.e., the
likelihood of establishment and the
potential impacts of cases that may
occur even without establishment) to
the United States via imports of live
bovines and bovine products from such
regions.
Additionally, this rule removes the
delay of applicability of provisions of
our January 2005 final rule regarding the
importation of meat, meat products, and
meat byproducts derived from bovines
in Canada that were 30 months of age
or older when slaughtered.
This regulatory impact analysis (RIA)
addresses expected economic effects of
allowing resumption of imports from
Canada of the above commodities.
Expected benefits and costs are
examined in accordance with Executive
Order 12866. Expected economic
impacts for small entities are also
evaluated, as required by the Regulatory
Flexibility Act. Our analysis indicates
that benefits of the rule will exceed
costs overall. Effects for Canadian and
other foreign entities are not addressed
in this analysis. However, the Agency
expects reestablished access to U.S.
markets to benefit Canadian producers
and suppliers of commodities included
in the rule.
Analytical Approach
The approach and models used in this
analysis are the same as were applied in
the preliminary RIA that we prepared
for our January 2007 proposed rule.
Impacts for cattle for feeding or for
immediate slaughter and impacts for
beef are quantitatively modeled. Impacts
for other affected commodities—
breeding cattle including dairy, vealers
and slaughter calves, bison, bovine
casings and small intestine products,
and bovine blood and blood products—
are examined largely qualitatively. For
the modeled cattle and beef, we project
a 5-year baseline, 2008–2012, against
which we measure expected price and
welfare effects of projected levels of
cattle and beef imports from Canada. We
evaluate price and welfare effects for the
three scenarios that were considered in
the preliminary RIA, as follows:
• Scenario 1: Allow imports of
Canadian cattle born on or after March
1, 1999;
• Scenario 2: Allow imports of
Canadian cattle unrestricted by date of
birth; and
• Scenario 3: The same as scenario 1,
with the addition of the resumption of
imports of beef from Canadian cattle
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slaughtered at 30 months or older
(called over-30-month, or OTM beef).
As a fourth scenario, we consider
imports of Canadian cattle unrestricted
by date of birth, with the resumption of
OTM beef imports. Projected imports
under this scenario 4 are described, but
the expected impacts are not evaluated,
for reasons explained below.
Beginning with baseline quantities
and prices, we compute effects of the
projected changes in imports from
Canada for four commodity categories:
Cull cattle/processing beef, feeder cattle,
fed cattle, and fed beef. The resumption
of cull cattle imports is expected to
affect the slaughter mix in Canada, and
that change in the slaughter mix will be
reflected in changes in the mix of
exports to the United States.
As part of this adjustment, for
example, we expect that more fed steers
and heifers will be slaughtered in
Canada and fewer will be exported to
the United States than if cull cattle
imports were not reestablished.
Canada’s cattle inventory increased
rapidly following the diagnosis of BSE
in a Canadian cow in May 2003 and
Canada’s subsequent loss of export
markets for cattle and beef. In response,
Canada’s slaughter capacity expanded.
Beginning in July 2005, with the
resumption of imports by the United
States of Canadian feeder cattle and fed
cattle, some Canadian plants continued
to utilize their expanded slaughter
capacity by shifting to increased cull
cattle slaughter. Canadian cull cattle
slaughter would likely continue to
expand if the United States were to
remain closed to imports of Canadian
cull cattle. However, with this rule, we
can expect some substitution in Canada
of cull cattle slaughter by fed cattle
slaughter.
Importation of fewer fed cattle from
Canada, all things equal, will cause the
price of fed cattle in the United States
to rise. We estimate the expected
increase in price and, because of the
price rise, the decrease in the quantity
of fed cattle demanded by U.S. slaughter
and packing establishments and the
increase in the quantity of fed cattle
supplied by U.S. feedlots. The analysis
yields measures of welfare change,
which in this example are in terms of
surplus losses for U.S. buyers and
surplus gains for U.S. sellers of fed
cattle.
For each of the first three scenarios,
we compute impacts for the modeled
commodities using the Baseline
Analysis System (BAS) model.29
29 A complete description of the model is
provided in: Forsythe, K.W. ‘‘An Economic Model
for Routine Analysis of the Welfare Effects of
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Impacts are also summed for each
scenario. The BAS model is a net trade,
non-spatial partial equilibrium model.
Partial equilibrium means that the
model results are based on maintaining
a commodity-price equilibrium in a
limited portion of an overall economy.
Commodities not explicitly included in
the model are assumed to have a
negligible influence on the results. The
simple summation of the separate
partial equilibrium results using the
BAS model does not take into account
market dynamics, but does provide a
reasonable approximation of the
combined welfare effects for each
scenario.
We also examine impacts more
broadly using a multi-sector model that
takes into account substitution among
livestock products in response to
relative price changes.30 This model
maps interactions among the grain,
animal, and animal products industries.
It takes into account substitution among
livestock products in response to
relative price changes, incorporates
foreign trade, and yields expected price
and revenue effects. The simulated
multi-sector impacts tend to be smaller
than the BAS model results because the
model linkages specified between the
livestock production and processing
sectors capture at least some of the
flexibility that industry enterprises
exhibit when adjusting to supply
shocks. These results support our
expectation that broader impacts of the
rule will be limited.
Baseline quantities and prices and
imports from Canada have been
projected by staff of USDA ERS, Market
and Trade Economics Division, Animal
Products, Grains, and Oil Seeds Branch,
based on their expert knowledge and
reference to ‘‘USDA Agricultural
Baseline Projections to 2016,’’ United
States Department of Agriculture,
Interagency Agricultural Projections
Regulatory Changes.’’ V3.00. U.S. Department of
Agriculture, Animal and Plant Health Inspection
Service, Veterinary Services, Centers for
Epidemiology and Animal Health. April 20, 2005
(draft). https://www.aphis.usda.gov/peer_review/
content/printable_version/
bas_model_econOnly_apr20.pdf
30 Four examples of studies based on this type of
model are: Paarlberg, P.L., A.H. Seitzinger, and J.G.
Lee, ‘‘Economic Impacts of Regionalization of a
Highly Pathogenic Avian Influenza Outbreak in the
United States,’’ Journal of Agricultural and Applied
Economics, forthcoming. Paarlberg, P.L.
‘‘Agricultural Export Subsidies and Intermediate
Goods Trade,’’ American Journal of Agricultural
Economics. 77, 1(1995): 119–128. Paarlberg, P.L.,
J.G. Lee, and A.H. Seitzinger. ‘‘Potential Revenue
Impact of an Outbreak of Foot-and-Mouth Disease
in the United States,’’ Journal of the American
Veterinary Medical Association. 220, 7(April 1,
2002): 988–992. Sanyal, K.K. and R.W. Jones. ‘‘The
Theory of Trade in Middle Products,’’ American
Economic Review. 72(1982): 16–31.
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Committee, Baseline Report OCE–2007–
1, February 2007.31
Projected Imports From Canada
Scenario 1. Table A shows the
projected changes in cattle and fed beef
imports from Canada under scenario 1
(in which imports of Canadian cattle
born on or after March 1, 1999, are
allowed). Under this scenario, cull cattle
imports from Canada are projected to
total 104,000 head in 2008 and average
147,800 head over the 5-year period of
analysis. These import numbers are
considerably smaller than were
projected in the preliminary RIA
because we now have a better
understanding of the extent to which
the birth-date restriction and ageverification requirement may limit the
number of cull cattle eligible for import.
Annual declines in feeder cattle and fed
cattle imports are projected to average
6,800 head and 56,800 head,
respectively. These declines correspond
to projected changes in the overall
Canadian cattle inventory, with the
import volumes for fed cattle further
adjusted downward to reflect greater
competition from Canadian packers due
to the resumption of U.S. imports of cull
cattle. Yearly fed beef imports are
projected to increase by an average of
45.8 million pounds, carcass weight
equivalent.
All of the changes under scenario 1
are small when compared to the
commodities’ projected U.S. baseline
supplies. The changes in imports for
feeder cattle, fed cattle, and fed beef
imports, in particular, are projected to
be only fractions of 1 percent of baseline
supplies. Under scenario 1, the number
of cull cattle projected to be imported in
2008 is less than 2 percent of projected
U.S. baseline cull cattle slaughter
quantities. Over the period of analysis,
cull cattle imports are projected to
average 2.5 percent of baseline
quantities. Cull cattle imports are
projected to increase in the latter years
of the analysis, and even more so in
subsequent years, as higher percentages
of Canada’s cull cattle inventory are able
to be verified as having been born on or
after March 1, 1999. A relative increase
in the number of cull cattle imported
over time is projected to be associated
with, in turn, a relative decrease in the
quantity of fed cattle imports and a
relative increase in the quantity of fed
beef imports.
Baseline projections over the 5-year
period, 2008–2012, show the United
States importing a little over 40 percent
of its supply of processing beef. A share
31 https://www.usda.gov/oce/commodity/
ag_baseline.htm
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of the cull cattle imported from Canada
will yield processing beef that will
substitute for processing beef that
otherwise would be imported from other
countries, while a share of the imported
cull cattle will yield processing beef that
will replace a quantity of processing
beef that would otherwise be
domestically supplied, as U.S.
producers respond to lower prices. The
remaining share of cull cattle imports
will yield processing beef that will
represent a net increase in U.S.
processing beef supplies.
We use 25 percent as the percentage
of cull cattle imports from Canada
projected to displace U.S. processing
beef imports from elsewhere. The 25
percent share is estimated using the
multi-sector model and takes into
account the interactions of the beef
processing sector with the beef cattle
and dairy cattle sectors. For comparison,
we also compute price and welfare
effects assuming that 50 percent of cull
cattle imported from Canada displace
processing beef imports, and assuming,
alternatively, that none of the imported
cull cattle displace processing beef
imports.
Scenario 2. In Table B, we show the
projected changes in cattle and fed beef
imports from Canada under scenario 2
(in which imports of Canadian cattle
unrestricted by birth date are allowed).
Under this scenario, imports of cull
cattle and changes in imports of fed
cattle and fed beef are all projected to
be much larger than in scenario 1.
Feeder cattle imports are projected to be
the same under all of the scenarios.
Projected cull cattle imports in scenario
2 average 459,800 head per year over the
period of analysis, or 7.8 percent of U.S.
baseline slaughter quantities. This
amount is more than three times cull
cattle imports projected in scenario 1.
The fed cattle and fed beef changes
remain a fraction of 1 percent of the U.S.
baseline supplies, but are also larger.
The increased number of cull cattle
imported in this scenario is projected to
be associated with larger declines in fed
cattle imports and larger increases in the
fed beef imports. We again estimate that
25 percent of cull cattle imports from
Canada under this scenario displace
processing beef imports from other
sources. Price and welfare analyses
assuming that 50 percent of the
imported cull cattle displace processing
beef imports and that none of the cull
cattle displace processing beef imports
are also presented.
Scenario 3. Table C shows the
projected changes in cattle and beef
imports from Canada under scenario 3
(in which imports of Canadian cattle
born on or after March 1, 1999, are
allowed and imports of OTM beef
resume). In scenario 3, impacts derive
from the resumption of OTM beef
imports as well as the cull cattle imports
from Canada. Projected cull cattle
imports are lower than in scenario 1
(averaging 106,000 head per year over
the 5-year period, compared to 147,800
head) because of the entry of OTM beef.
Similarly, changes in projected fed
cattle and fed beef imports are
somewhat smaller than the changes
projected in scenario 1. Processing beef
imports from Canada under scenario 3
are projected to average 254.6 million
pounds per year, carcass weight
equivalent, or about 4.1 percent of the
U.S. baseline supply. The quantity of
processing beef imported is projected to
decline and the quantity of cull cattle
imported is projected to increase in the
latter years of the 5-year period, as an
increasing number of cull cattle become
eligible for importation—i.e., can be
verified as having been born on or after
March 1, 1999. Under scenario 3, and
considering imports of cull cattle (based
on the cattle’s processing beef
equivalence) and processing beef as a
single market, 77 percent of cull cattle
and processing beef imports from
Canada are projected to enter the United
States as OTM beef over the 5-year
period of the analysis, while 23 percent
of these imports are projected to enter
as cull cattle. Consistent with scenarios
1 and 2, we use 25 percent as the share
of the cull cattle and OTM beef imports
from Canada that displaces processing
beef imports from other countries. We
also present the price and welfare
effects assuming that either 50 percent
or none of the cull cattle and OTM beef
imports from Canada displace
processing beef imports from elsewhere.
Scenario 4. In table D, we show the
projected changes in cattle and fed beef
imports from Canada under scenario 4
(in which imports of Canadian cattle
unrestricted by birth date are allowed
and imports of OTM beef resume). As in
scenario 2, imports of cull cattle and
changes in imports of fed cattle and fed
beef are all projected to be larger than
in scenarios 1 and 3.
Projected cull cattle imports in
scenario 4 average 328,200 head per
year over the period of analysis, or 5.5
percent of U.S. baseline slaughter
quantities. The fed cattle and fed beef
changes remain a fraction of 1 percent
of the U.S. baseline supplies.
TABLE A.—PROJECTED CHANGES IN IMPORTS OF CULL CATTLE, FEEDER CATTLE, FED CATTLE, FED BEEF, AND PROCESSING BEEF FROM CANADA UNDER SCENARIO 1, AND PROJECTED CHANGES IN IMPORTS FROM CANADA AS A PERCENTAGE OF THE PROJECTED U.S. BASELINE SUPPLIES, 2008–2012
pwalker on PROD1PC71 with RULES2
2008
Projected changes in imports from Canada:
Cull cattle (thousand head) ......................................................................................................
Feeder cattle (thousand head) .................................................................................................
Fed cattle (thousand head) ......................................................................................................
Fed beef (million pounds, carcass weight equivalent) .............................................................
Processing beef (million pounds, carcass weight equivalent) .................................................
Projected changes in imports from Canada as a percentage of the projected U.S. baseline supply:
Cull cattle ..................................................................................................................................
Feeder cattle .............................................................................................................................
Fed cattle ..................................................................................................................................
Fed beef ....................................................................................................................................
Processing beef ........................................................................................................................
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2009
2010
2011
2012
104
¥1
¥30
24
0
110
9
¥4
3
0
113
¥5
¥43
35
0
187
¥16
¥93
75
0
225
¥21
¥114
92
0
1.8%
nil
¥0.1%
0.1%
0
1.9%
nil
nil
nil
0
1.9%
nil
¥0.1%
0.2%
0
3.1%
nil
¥0.3%
0.3%
0
3.7%
¥0.1%
¥0.4%
0.4%
0
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53369
TABLE B.—PROJECTED CHANGES IN IMPORTS OF CULL CATTLE, FEEDER CATTLE, FED CATTLE, FED BEEF, AND PROCESSING BEEF FROM CANADA UNDER SCENARIO 2, AND PROJECTED CHANGES IN IMPORTS FROM CANADA AS A PERCENTAGE OF THE PROJECTED U.S. BASELINE SUPPLIES, 2008–2012
2008
Projected changes in imports from Canada:
Cull cattle (thousand head) ......................................................................................................
Feeder cattle (thousand head) .................................................................................................
Fed cattle (thousand head) ......................................................................................................
Fed beef (million pounds, carcass weight equivalent) .............................................................
Processing beef (million pounds, carcass weight equivalent) .................................................
Projected changes in imports from Canada as a percentage of the projected U.S. baseline supply:
Cull cattle ..................................................................................................................................
Feeder cattle .............................................................................................................................
Fed cattle ..................................................................................................................................
Fed beef ....................................................................................................................................
Processing beef ........................................................................................................................
2009
2010
2011
2012
459
¥1
¥119
96
0
459
9
¥91
74
0
459
¥5
¥129
105
0
460
¥16
¥161
131
0
462
¥21
¥173
140
0
8.2%
nil
¥0.4%
0.4%
0
7.8%
nil
¥0.3%
0.3%
0
7.6%
nil
¥0.4%
0.5%
0
7.6%
nil
¥0.5%
0.6%
0
7.6%
¥0.1
¥0.6%
0.6%
0
TABLE C.—PROJECTED CHANGES IN IMPORTS OF CULL CATTLE, FEEDER CATTLE, FED CATTLE, FED BEEF, AND PROCESSING BEEF FROM CANADA UNDER SCENARIO 3 AND PROJECTED CHANGES IN IMPORTS FROM CANADA AS A PERCENTAGE OF THE PROJECTED U.S. BASELINE SUPPLIES, 2008–2012
2008
Projected changes in imports from Canada:
Cull cattle (thousand head) ......................................................................................................
Feeder cattle (thousand head) .................................................................................................
Fed cattle (thousand head) ......................................................................................................
Fed beef (million pounds, carcass weight equivalent) .............................................................
Processing beef (million pounds, carcass weight equivalent) .................................................
Projected changes in imports from Canada as a percentage of the projected U.S. baseline supply:
Cull cattle ..................................................................................................................................
Feeder cattle .............................................................................................................................
Fed cattle ..................................................................................................................................
Fed beef ....................................................................................................................................
Processing beef ........................................................................................................................
2009
2010
2011
2012
75
¥1
¥23
18
277
79
9
4
¥3
273
81
¥5
¥34
28
272
134
¥16
¥80
65
234
161
¥21
¥98
79
217
1.3%
nil
¥0.1%
0.1%
4.7%
1.3%
nil
nil
nil
4.5%
1.3%
nil
¥0.1%
0.1%
4.4%
2.2%
nil
¥0.3%
0.3%
3.7%
2.7%
¥0.1
¥0.3%
0.3%
3.4%
TABLE D.—PROJECTED CHANGES IN IMPORTS OF CULL CATTLE, FEEDER CATTLE, FED CATTLE, FED BEEF, AND PROCESSING BEEF FROM CANADA UNDER SCENARIO 4, AND PROJECTED CHANGES IN IMPORTS FROM CANADA AS A PERCENTAGE OF THE PROJECTED U.S. BASELINE SUPPLIES, 2008–2012
2008
Projected changes in imports from Canada:
Cull cattle (thousand head) ......................................................................................................
Feeder cattle (thousand head) .................................................................................................
Fed cattle (thousand head) ......................................................................................................
Fed beef (million pounds, carcass weight equivalent) .............................................................
Processing beef (million pounds, carcass weight equivalent) .................................................
Projected changes in imports from Canada as a percentage of the projected U.S. baseline supply:
Cull cattle ..................................................................................................................................
Feeder cattle .............................................................................................................................
Fed cattle ..................................................................................................................................
Fed beef ....................................................................................................................................
Processing beef ........................................................................................................................
pwalker on PROD1PC71 with RULES2
Effects for Commodities Not Analyzed
Using the BAS Model
Five categories of commodities that
will be affected by this rule have not
been included in the modeled
quantitative analysis described above.
They are: Breeding cattle, including
dairy; vealers and slaughter calves;
bison; bovine casings and small
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intestine products; and bovine blood
and blood products. Projected imports
of breeding cattle including dairy, and
projected changes in imports of vealers,
slaughter calves, and bison, are
relatively small, suggesting that impacts
on affected U.S. entities will not be
significant. For bovine casings, small
intestine products, and blood and blood
PO 00000
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2009
2010
2011
2012
328
¥1
¥86
70
94
328
9
¥58
47
94
327
¥5
¥96
78
94
328
¥16
¥129
104
94
330
¥21
¥140
114
95
5.8%
nil
¥0.3%
0.3%
1.6%
5.6%
nil
¥0.2%
0.2%
1.5%
5.4%
nil
¥0.3%
0.3%
1.5%
5.4%
nil
¥0.4%
0.5%
1.5%
5.4%
¥0.1%
¥0.5%
0.5%
1.5%
products, the analysis is constrained by
a scarcity of information about the
quantities that would be imported and
levels of U.S. production and
consumption.
With regard to dairy producers, we do
not expect imports of dairy cattle from
Canada to add significantly to the U.S.
herd, but rather to serve as an additional
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source of replacement animals. From
1992 to 2002, U.S. producers annually
raised about 4.1 million dairy
replacement heifers and about 5.9
million beef replacement heifers. The
average number of Canadian breeding
cattle imported during that period
(including bulls) totaled only 0.5
percent of these combined quantities.
The breeding cattle imports from
Canada during this period represented
about 1.1 percent of dairy heifer
replacements and less than 0.1 percent
of beef heifer replacements. Imports of
dairy cows and heifers from Canada are
projected to be similar to their historic
levels, 1992–2002, averaging 47,800
head per year over the period of analysis
in all of the scenarios.
Analysis using the multi-sector model
indicates that, in scenario 3, dairy
producers may experience price
declines of 1.3 to 1.7 percent for dairy
cattle due to the small number projected
to be imported from Canada. These
imports translate into an increase in
U.S. milk production of 0.1 percent or
less, and a decline in the price of milk
and increase in consumer surplus of less
than 0.1 percent. As sellers of cull
cattle, dairy producers as well as beef
producers are expected to be negatively
affected by the price decline for cull
cattle due to this rule.
We expect market effects for vealers
and slaughter calves to be insignificant,
given the small change in the number
projected to be imported from Canada.
The decline in imports is projected in
scenario 3 to average only 6 percent, or
3,000 head per year.
A larger number of bison are projected
to be imported than was projected in the
preliminary RIA. Reestablished imports
of Canadian breeding bison will be the
principal impact of this rule for that
industry. Yearly imports of breeding
bison are projected to average 1,200
head, and are expected to represent
about 1 percent of U.S. breeding bison,
assuming the composition of the
national bison herd is similar to that of
the national cattle herd.
This rule may directly affect the U.S.
supply of bovine casings and small
intestine products through resumption
of imports from Canada, and may affect
it indirectly through changes in U.S.
cattle slaughter numbers and the
reestablished importation of Canadian
bovine small intestines, minus the distal
ileum. For scenario 3, the annual supply
of bovine casings produced from
additional U.S. cattle slaughter is
projected to increase on average over the
period of analysis by less than 0.2
percent.
Fetal bovine serum (FBS) is the most
important blood product that will be
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affected by this rule. Resumption of
commercial imports of FBS from
Canada, directly as serum and indirectly
through increased U.S. pregnant cow
slaughter, is expected to benefit FBS
users, given current strong demand for
this blood product in the United States.
Expected Impacts for Modeled
Commodities
In this summary, prices and welfare
impacts are expressed in 2007 dollars;
price and quantity averages and
percentage averages are over the 5-year
period of analysis, 2008–2012;
annualized values are discounted at 3
percent; and beef prices and quantities
are in carcass weight equivalent.
Percentage changes in prices and
estimated welfare effects are shown in
table E.
Scenario 1. In this scenario, buyers of
cull cattle and processing beef can be
expected to benefit from welfare gains
and sellers of cull cattle and processing
beef can be expected to bear welfare
losses due to the cull cattle imports. For
this commodity, the estimated
annualized consumer gains are $90.3
million, producer losses are $53.2
million, and net benefits are $37.1
million.
Welfare changes for the cull cattle/
processing beef category dominate the
modeled effects in all of the scenarios.
The relatively large impacts are not
unexpected, given that this is the one
modeled commodity category for which
imports from Canada would be newly
reestablished and projected changes
from the baseline are much larger than
for the other commodities. The numbers
of cull cattle projected to be imported in
scenario 1, averaging 124,800 cows and
23,000 bulls and stags per year, are
much larger than the projected average
annual declines in imports of Canadian
fed cattle (56,800 head) and feeder cattle
(6,800 head).
Another reason the welfare effects
computed for the cull cattle/processing
beef category are large is the inelastic
demand (¥0.40) compared to the price
elasticities of demand—i.e., buyers’
responsiveness to changes in price—for
the other modeled commodities (feeder
cattle, –0.88; fed cattle, ¥0.76; fed beef,
¥0.60). In the preliminary RIA, we
examined the significance of processing
beef’s more inelastic demand by
considering welfare changes for the cull
cattle/processing beef category when a
price elasticity of demand of ¥0.60 is
used, that is, the same elasticity as for
fed beef. This exercise found that all
impacts—consumer gains, producer
losses, net benefits, and price declines—
are reduced by nearly one-fifth when a
price elasticity of demand of ¥0.60 is
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used in place of ¥0.40. The price
elasticity of demand is an important
determinant of the magnitude of welfare
and price changes for the cull cattle/
processing beef category.
Lastly, the large difference between
consumer welfare gains and producer
welfare losses for the cull cattle/
processing beef category can be
attributed to the fact that the United
States is projected to import about 40
percent of its supply of processing beef
over the period of analysis. In modeling
the welfare effects, demand (defined as
U.S. consumption) is much larger than
supply (defined as U.S. production
minus exports). Consequently the
change in consumer surplus is large
compared to the change in producer
surplus because the effects are estimated
only for U.S. entities.
Slightly fewer feeder cattle are
projected to be imported from Canada in
scenario 1 than would otherwise enter,
and the analysis indicates small gains in
producer welfare (higher prices and less
competition from Canadian suppliers)
and small losses in consumer welfare
for this commodity (higher prices and
fewer feeder cattle available for
purchase). Estimated annualized values
are producer gains of $3.6 million,
consumer losses of $3.8 million, and net
losses of $0.2 million.
As with feeder cattle, fewer fed cattle
are projected to be imported under
scenario 1 than would otherwise be
imported. Once again, producers (sellers
of fed cattle for slaughter) would benefit
from welfare gains and consumers
(buyers of fed cattle for slaughter) would
bear welfare losses. Estimated
annualized values are producer gains of
$43.6 million, consumer losses of $44.7
million, and net losses of about $1.1
million.
Scenario 1 is projected to result in
increased imports of Canadian fed beef
ranging from an additional 3 million
pounds in 2009 to 92 million pounds in
2012. Estimated annualized values are
consumer gains of $48.8 million,
producer losses of $46.8 million, and
net gains of $2 million.
The analysis shows annualized
combined welfare changes under
scenario 1 as consumer gains of $90.6
million and producer losses of $52.7
million, yielding net benefits of $37.9
million. As can be seen in table E, the
combined annualized values of
consumer welfare losses for feeder cattle
and fed cattle are similar to the
consumer welfare gains for fed beef.
Combined consumer welfare gains are
very similar to the consumer welfare
gains estimated for the cull cattle/
processing beef category. A similar but
opposite outcome is evident with
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respect to producer welfare changes,
with combined gains for feeder cattle
and fed cattle somewhat larger than the
producer welfare losses for fed beef. The
result is combined producer welfare
losses that are close to the producer
welfare losses estimated for cull cattle/
processing beef. Under scenario 1, the
combined annualized net welfare
benefits, $37.9 million, are only slightly
53371
more than the $37.1 million in net
benefits estimated for cull cattle/
processing beef.
TABLE E.—COMPARISON OF PERCENTAGE PRICE CHANGES AND ANNUALIZED WELFARE EFFECTS FOR SCENARIOS 1, 2,
AND 3 BY COMMODITY CATEGORY, 2008–2012, DISCOUNTED AT 3 PERCENT, 2007 DOLLARS
Commodity category
Percentage
change in
price
Scenario
Change in
consumer
welfare
Change in
producer welfare
Net welfare
change
Thousand dollars
Cull cattle/Processing beef ..................................................
1
2
3
1
2
3
1
2
3
1
2
3
1
2
3
Feeder cattle ........................................................................
Fed cattle .............................................................................
Fed beef ...............................................................................
Categories combined ...........................................................
¥1.4%
¥4.5%
¥4.5%
nil
nil
nil
0.1%
0.3%
0.1%
¥0.1%
¥0.3%
¥0.1%
........................
........................
........................
90,307
286,936
286,912
¥3,795
¥3,795
¥3,795
¥44,703
¥107,513
¥36,263
48,800
117,459
39,791
90,609
293,087
286,645
¥53,207
¥165,615
¥165,603
3,605
3,605
3,605
43,636
105,101
35,388
¥46,757
¥112,426
¥38,131
¥52,723
¥169,335
¥164,741
37,100
121,320
121,308
¥190
¥190
¥190
¥1,066
¥2,412
¥874
2,044
5,033
1,660
37,888
123,751
121,904
pwalker on PROD1PC71 with RULES2
The three import scenarios considered in this table are (1) Canadian cattle born on or after March 1, 1999; (2) Canadian cattle unrestricted by
date of birth; and (3) Canadian cattle born on or after March 1, 1999, plus resumption of imports of meat from Canadian cattle slaughtered at 30
months or older. The percentage change in price is the average annual change over the 5-year period. Welfare changes may not sum due to
rounding.
Scenario 2. Because of the
significantly larger number of cull cattle
projected to be imported in scenario 2,
the estimated price and welfare effects
are also much larger than for scenario 1.
Table E shows these differences, with
the percentage changes in price about
three times greater in all cases (other
than for feeder cattle, for which imports
are projected to be the same in all
scenarios). Whereas the combined net
benefit in scenario 1 is estimated to be
an annualized $37.9 million, in scenario
2 it is $123.8 million.
As described in the risk assessment,
transmission of BSE requires that
bovines ingest feed that contains the
infectious agent. The OIE establishes
standards for the international trade in
animals and animal products. It
recommends that cattle be imported
from a controlled risk region for BSE
only if the cattle selected for export
were born after that date from which a
ban on the feeding of ruminants with
meat-and-bone meal and greaves (the
residue left after animal fat or tallow has
been rendered) derived from ruminants
had been effectively enforced. In May
2007, the OIE classified both the United
States and Canada as BSE controlled
risk regions.
On August 4, 1997, Canada issued
regulations prohibiting the use of
mammalian protein in ruminant feeds.
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Implementation of the feed ban was a
gradual process, with producers, feed
mills, retailers, and feed manufacturers
given grace periods before they were
required to be in full compliance with
the regulations. It is believed that this
implementation period may have lasted
6 months, making February 1998 a more
realistic date on which the ban can be
considered to have gone into effect.
APHIS considers that a period of 1
year following the full implementation
of the feed ban allowed sufficient time
for the measures taken by Canada to
have their desired effect. Therefore,
APHIS concludes that there is an
extremely low likelihood that cattle
born in Canada on or after March 1,
1999, will have been exposed to the BSE
agent via feed. Therefore, these animals
have an extremely low likelihood of
being infected and can be imported into
the United States for any purpose.
We do not have a quantitative
estimate of the additional risk posed by
importation of Canadian cattle born
before March 1, 1999. The importance of
a feed ban as a risk mitigation measure
is demonstrated in science and
experience, and is incorporated into the
OIE guidelines. We conclude that there
could be some degree of increased
likelihood of BSE infectivity entering
the United States via imports of live
bovines from Canada under scenario 2,
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compared to the very low likelihood
posed in scenario 1, because of the
greater likelihood of cattle born prior to
the effective enforcement of a feed ban
having been exposed to infectivity.
Scenario 3. The price and welfare
effects under scenario 3 are similar to
the effects under scenario 2 for cull
cattle/processing beef, but more like the
scenario 1 effects for fed cattle and fed
beef (table E). This outcome is expected
because scenario 3 includes
reestablishment of OTM beef imports
from Canada. Combined net welfare
benefits for scenarios 2 and 3 are very
similar, with the projected cull cattle
imports in scenario 2 and the projected
imports of cull cattle and OTM beef in
scenario 3 both based on cattle and beef
import quantities prior to May 2003.
The additional quantities of cull cattle/
processing beef in scenarios 2 and 3 are
essentially the same, entering as live
cattle in scenario 2 and as beef in
scenario 3.
The BSE risk mitigations under
scenario 3 are comparable to those
under scenario 1. The restriction on live
bovine imports by date of birth, age
verification, and other safeguard
measures are the same in both cases.
Consequently, as in scenario 1, the
likelihood of BSE infectivity entering
the United States via imports of live
bovines from Canada in this scenario is
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extremely low. Resumption of OTM beef
imports from Canada will not affect the
likelihood of BSE infectivity entering
the United States because SRMs will be
removed and disposed of in Canada.
Scenario 4. A fourth scenario, as
indicated above, would be to allow
entry of Canadian cattle unrestricted by
birth date, along with resumption of
OTM beef imports from Canada. A
quantitative analysis of expected price
and welfare effects for this particular
scenario was not performed. When we
compare projected imports under this
scenario with those projected for
scenario 3, we find the differences in
combined cattle and beef imports to be
very small and conclude that the
welfare effects for this scenario would
be very similar to the effects of scenario
3.
Cull cattle imports from Canada are
projected to average about 328,000 head
per year under scenario 4, compared to
106,000 head per year under scenario 3.
Conversely, annual processing beef
imports under scenario 4 are projected
to average 94 million pounds, carcass
weight equivalent, compared to 255
million pounds for scenario 3.
Similar differences between the two
scenarios are projected for fed cattle and
fed beef imports. The larger number of
cull cattle that would be imported from
Canada under scenario 4 could be
expected to be associated with increased
fed cattle slaughter in Canada, with
fewer fed cattle and more fed beef
exported to the United States. Under
scenario 4, fed cattle imports from
Canada are projected to average about
624,000 head per year, compared to
679,000 head per year under scenario 3.
Annual fed beef imports under scenario
4 are projected to average 992 million
pounds, compared to 947 million
pounds for scenario 3.
The average annual net difference
between scenarios 3 and 4 in projected
cull cattle and processing beef imports
from Canada, after converting the cull
cattle to processing beef, is about
700,000 pounds (330.8 million pounds
in scenario 3, and 330.1 million pounds
in scenario 4). This amount represents
about 0.2 percent of projected cull
cattle/processing beef imports under
scenario 3. For fed cattle and fed beef
imports from Canada, the average
annual net difference between scenarios
3 and 4 after converting the fed cattle to
fed beef, is about 1.3 million pounds
(1,483.7 million pounds in scenario 3,
and 1,485.0 million pounds in scenario
4). This amount represents about 0.1
percent of the projected fed cattle and
fed beef imports under scenario 3.
Hence, we conclude that the overall
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Jkt 211001
welfare effects of scenario 4 would be
very similar to those for scenario 3.
Effects on Small Entities
There were no significant issues
raised in public comment on the initial
regulatory flexibility analysis (RFA) for
this rulemaking. However, as described
below, the majority of businesses that
may be affected by this rule are small
entities. Therefore, while none of the
comments received on the proposed
rule raised specific issues regarding the
initial RFA, comments on the
preliminary RIA can be inferred to
express small-entity concerns.
Topics that received public comment
and that concerned the estimated
economic impacts of the proposed rule
included modeling issues; the timing of
the rule’s implementation;
consequences of a BSE occurrence; and
impacts of the rule for consumers, cowcalf producers, the dairy industry, and
the packing industry, and on beef
exports. These comments are addressed
in the Agency’s responses that are
included as part of the final rule.
Small entities comprise the majority
of the establishments engaged in the
production, processing, and sale of the
commodities affected by this rule. These
small entities number at least in the
hundreds of thousands, with cow-calf
and dairy producers comprising the
largest single industry sector share. The
entities are classified within the
following industries according to the
North American Industry Classification
System: Beef Cattle Ranching and
Farming (NAICS 112111), Dairy Cattle
and Milk Production (NAICS 112120),
All Other Animal Production (NAICS
112990), Cattle Feedlots (NAICS
112112), Animal (except Poultry)
Slaughtering (NAICS 311611), Meat
Processed from Carcasses (NAICS
311612), Meat and Meat Product
Merchant Wholesalers (NAICS 424470),
Supermarkets and Other Grocery
(except Convenience) Stores (NAICS
445110), Meat Markets (NAICS 445210),
In-Vitro Diagnostic Substance
Manufacturing (NAICS 325413), and
Biological Product (except Diagnostic)
Manufacturing (NAICS 325414).
We are unable to determine the extent
to which cull cattle prices may fall
because of the rule. Assuming that the
price decline for cull cattle is
proportional to the estimated price
decline for processing beef, cow-calf
and dairy producers in scenario 3 may
experience a fall in price for cull cattle
of 4.7 percent in 2008, and an average
price decline of 4.5 percent ($4.61 per
cwt). To place this average price decline
in perspective, we consider the effect it
may have on gross earnings of small-
PO 00000
Frm 00060
Fmt 4701
Sfmt 4700
entity cow-calf operations. Based on
data from the 2002 Census of
Agriculture, the average value of cattle
and calves sold by small-entity beef cow
operations was about $26,600.32 The
projected 2008 price for a culled cow is
$54.19 per cwt.33 Assuming the cow
weighs 1,100 pounds, its price in 2008
would be $596.09 per head. A 4.7
percent decline would result in a price
of $568.07. Presumably, most of a cowcalf operation’s revenue is earned from
the sale of calves. If one-half of an
operation’s revenue were to derive from
the sale of cull cattle, the reduction in
revenue attributable to the decline in
the price of cull cattle in scenario 3
would total about $625 for the year.34
For dairy enterprises, the expected
price decline for cull cattle because of
imports from Canada is expected to
have a small effect on their incomes
because most revenue (over 86 percent
in 2002) is earned from the sale of milk
and other dairy products.35 The average
per animal value of cattle and calves
sold by small-entity dairy cow
operations in 2002 was about $453. A
price decline of 4.7 percent,
notwithstanding the fact that not all of
the animals sold would be cull cattle,
would mean a decrease in annual
revenue for the average small-entity
dairy operation of about $1,040,
assuming no change in the number of
cattle sold.36 This forgone income
would represent a decline in average
revenue of about 0.6 percent.37
The scenario 3 analysis indicates that
decreases in the price of fed beef due to
increased fed beef imports from Canada
are expected to be very small, resulting
in a loss for the average meat packing
and processing establishment of less
than 0.2 percent of average revenue (18
cents per cwt, with projected baseline
fed beef prices averaging $151.80 per
cwt). Effects for those packers and
processors that utilize processing beef
will be larger, due to the resumption of
cull cattle and OTM beef imports from
32 USDA, NASS. 2002 Census of Agriculture,
Volume 1, Chapter 1, Table 16. The $26,000 average
is for operations with fewer than 1,000 head.
https://www.nass.usda.gov/Census_of_Agriculture/
index.asp
33 Boning utility cow (Sioux Falls) nominal price.
34 ($26,600/2) (0.047) = $625.10.
35 USDA, NASS, 2002 Census of Agriculture,
Volume 1, Chapter 1, Table 17. For small-entity
producers, revenue from cattle and calf sales totaled
$1.7 billion and revenue from dairy product sales
totaled $11.2 billion. https://www.nass.usda.gov/
Census_of_Agriculture/index.asp
36 In 2002, the average revenue from cattle sales
for small-entity dairy operations was $22,197 ($453
per head multiplied by 49 head). ($22,197)(0.047)
= $1,043.26.
37 $1,043 divided by $175,912 (average income
for small dairy farms from combined dairy product
and cattle sales) equals 0.59 percent.
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Federal Register / Vol. 72, No. 180 / Tuesday, September 18, 2007 / Rules and Regulations
Canada. Annual prices of processing
beef are expected to fall by an average
of $4.61 per cwt in scenario 3. This
decline in price will benefit
establishments that use processing beef
to produce ground beef for the
wholesale market. Conversely,
establishments that sell processing beef
will be negatively affected by the
expected price decline.
In response to public comments on
the preliminary RIA, we include an
evaluation of welfare effects by industry
sector for scenario 3. While this
evaluation is admittedly broad, it
provides an indication of the extent to
which major sectors of the cattle and
beef industries may be affected. We
group the entities that we expect to be
directly affected into four generalized
categories: cow-calf and dairy
producers, feedlot establishments,
slaughter and packing establishments,
and wholesaler and successive
establishments. Admittedly, this simple
categorization does not capture the
many complexities of the cattle and beef
industries, but it does provide a level of
specification sufficient for examining
expected effects for the industries’
principal stages of economic activity. In
reality, businesses combine the
slaughter, packing, processing, and
wholesaling functions in various ways.
This consideration of sector-level effects
indicates that cow-calf and dairy
producers and slaughter and packing
establishments are expected to incur net
welfare losses, while feedlots and
wholesalers are expected to accrue net
welfare gains.
Currently, bovines imported from
Canada are restricted to animals that are
slaughtered at less than 30 months of
age. Bovines not imported for
immediate slaughter must be moved
from the port of entry to a feedlot in a
sealed means of conveyance and from
the feedlot to a recognized slaughtering
establishment again in a sealed means of
conveyance. The animals may not be
moved to more than one feedlot. With
this rule, these movement restrictions
will no longer be imposed. Canadian
bovines imported other than for
immediate slaughter will be able to be
moved any number of times to any
destinations in unsealed means of
conveyance.
Under this rule, feeder bovines
imported from BSE minimal-risk regions
will not need to be accompanied by
APHIS Form VS 17–130, which
currently is used to identify the feedlot
of destination. (The name of the
individual responsible for the
movement of an imported animal and
individual identification of the animal
will still be required information on the
VerDate Aug<31>2005
19:35 Sep 17, 2007
Jkt 211001
accompanying health certificate.) APHIS
estimates that the time saved by entities
no longer needing to acquire APHIS
Form VS 17–130 will total
approximately 40,000 hours per year.38
Also under this rule, bovines of
Canadian origin moved from a U.S.
feedlot to a slaughtering establishment
will not need to be accompanied by
APHIS Form VS 1–27. APHIS estimates
the same total time savings by entities
no longer needing to acquire APHIS
Form VS 1–27: 40,000 hours per year.
Removal of these movement and
paperwork requirements will benefit
buyers and sellers of Canadian-origin
bovines. Many of the beneficiaries are
likely to be small entities, given their
predominance among beef and dairy
operations and feedlot establishments.
Affected businesses will be able to take
advantage of a broader range of
transactional opportunities than
previously. For example, the sale of a
young steer first for backgrounding, then
for confined feeding at one or more
facilities, and finally for slaughter may
enable the original and subsequent
owners of the animal to better maximize
returns compared to current marketing
possibilities. While we are not able to
quantify impacts of removing current
movement restrictions on Canadian
cattle imports, we expect their removal
will benefit the cattle industry acrossthe-board.
The Agency has identified
alternatives to the rule and analyzed
them in this RIA. We have found that
the chosen alternative (scenario 3) best
strikes the balance of continuing to
provide an acceptable level of
protection against BSE infectivity
entering the United States via imports of
live bovine and bovine product imports,
while removing unnecessary
prohibitions on the importation of
certain commodities from Canada.
Without this rule, restrictions on U.S.
importation of certain Canadian bovine
commodities that are without scientific
merit would continue. With this rule,
importation of these Canadian
commodities will be allowed to resume
under certain conditions and the BSE
risk to the United States via imports of
live bovines and bovine products from
Canada will be negligible.
Small Business Regulatory Enforcement
Fairness Act of 1996
This rule has been designated by the
Administrator, Office of Information
38 This approximation is based on 1,000 entities
filling out Form VS 17–130 on 20 occasions per
year, with each form requiring two hours. The
estimated total time saved by not having to
complete Form VS 1–27 is calculated on this same
basis.
PO 00000
Frm 00061
Fmt 4701
Sfmt 4700
53373
and Regulatory Affairs, Office of
Management and Budget, as a major rule
under the Small Business Regulatory
Enforcement Fairness Act of 1996 (5
U.S.C. 801–808). Accordingly, the
effective date of this rule has been
delayed the required 60 days pending
congressional review.
Executive Order 12988
This final rule has been reviewed
under Executive Order 12988, Civil
Justice Reform. This rule: (1) Preempts
all State and local laws and regulations
that are inconsistent with this rule; (2)
has no retroactive effect; and (3) does
not require administrative proceedings
before parties may file suit in court
challenging this rule.
National Environmental Policy Act
An environmental assessment and
finding of no significant impact have
been prepared for this final rule. The
environmental assessment provides a
basis for the conclusion that the
importation of live bovines and of
bovine products as specified in this rule
will not have a significant impact on the
quality of the human environment.
Based on the finding of no significant
impact, the Decisionmaker of the
Animal and Plant Health Inspection
Service has determined that an
environmental impact statement need
not be prepared.
The environmental assessment and
finding of no significant impact were
prepared in accordance with: (1) The
National Environmental Policy Act of
1969 (NEPA), as amended (42 U.S.C.
4321 et seq.), (2) regulations of the
Council on Environmental Quality for
implementing the procedural provisions
of NEPA (40 CFR parts 1500–1508), (3)
USDA regulations implementing NEPA
(7 CFR part 1b), and (4) APHIS’ NEPA
Implementing Procedures (7 CFR part
372).
The environmental assessment and
finding of no significant impact may be
viewed on the APHIS Web site (https://
www.aphis.usda.gov/newsroom/
hot_issues/bse/index.shtml), or be
obtained by contacting the person listed
under FOR FURTHER INFORMATION
CONTACT. Copies of the environmental
assessment and finding of no significant
impact are also available for public
inspection at USDA, room 1141, South
Building, 14th Street and Independence
Avenue, SW., Washington, DC, between
8 a.m. and 4:30 p.m., Monday through
Friday, except holidays. Persons
wishing to inspect copies are requested
to call ahead on (202) 690–2817 to
facilitate entry into the reading room. In
addition, copies may be obtained by
E:\FR\FM\18SER2.SGM
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53374
Federal Register / Vol. 72, No. 180 / Tuesday, September 18, 2007 / Rules and Regulations
writing to the individuals listed under
FOR FURTHER INFORMATION CONTACT.
Paperwork Reduction Act
This final rule contains no new
information collection or recordkeeping
requirements under the Paperwork
Reduction Act of 1995 (44 U.S.C. 3501
et seq.).
pwalker on PROD1PC71 with RULES2
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Affirmation of Interim Final Rules with
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Specified Risk Materials for Human Food
and Requirements for the Disposition of
Non-Ambulatory Disabled Cattle;
Prohibition of the Use of Certain Stunning
Devices Used to Immobilize Cattle During
Slaughter. July 13. (https://
www.fsis.usda.gov/Regulations_&_Policies/
federal_register_publications_&_related_
documents/index.asp)
Fox, J., and H.H. Peterson. (2004). Risks and
Implications of bovine spongiform
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encephalopathy for the United States:
Insights from other countries. Food Policy
29 (2004): 45–60.
Giovannini, A., L. Savini, A. Conte, and G.L.
Fiore. (2005). Comparison of BSE
Prevalence Estimates from EU Countries
for the Period July to December 2001 to the
OIE and EU GBR Classifications. Journal of
Veterinary Medicine, Series B 52: 262–271.
Heim, D., and U. Kihm. (2003). Risk
management of transmissible spongiform
encephalopathies in Europe. Rev. Sci.
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Heres, L., I. Elbers, B. Schreuder, and F. van
Zijderveld. (2005). BSE in Nederland.
Wageningen, CIDC-Lelystad. (www.cidclelystad.wur.nl/NR/rdonlyres/C965BF6E–
16C1–446A–B3D2–64DB72616494/11387/
BSEinNederland.pdf)
Hill, W. (2005). Review of the Evidence for
the Occurrence of ‘BARB’ BSE Cases in
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animalh/bse/pdf/hillreport.pdf)
Hoffman, C., U. Ziegler, A. Buschmann, A.
Weber, L. Kupfer, A. Oelschlegel, B.
Hammerschmidt, and M.H. Groschup.
(2007). Prions spread via the autonomic
nervous system from the gut to the central
nervous system in cattle incubating bovine
spongiform encephalopathy. J. Gen.
Virology 88(3): 1048–1055. March.
Iwamaru, Y., Y. Okubo, T. Ikeda, H. Hayashi,
M. Imamura, T. Yokoyama, and M.
Shinagawa. (2005). PrPSc distribution of a
natural case of bovine spongiform
encephalopathy. Kitamoto T, ed. Prions:
Food and Drug Safety. Springer-Verlag,
New York.
Iwata, N., Y. Sato, Y. Higuchi, K. Nohtomi,
N. Nagata, H. Hasegawa, M. Tobiume, Y.
Nakamura, K. Hagiwara, H. Furuoka, M.
Horiuchi, Y. Yamakawa, and T. Sata.
(2006). Distribution of PrPSc in Cattle with
Bovine Spongiform Encephalopathy
Slaughtered at Abattoirs in Japan. Jpn. J.
Infect. Dis. 59(2): 100–107. (https://
www.nih.go.jp/JJID/59/100.pdf)
Kuchler, F., and A. Tegene. ‘‘Did BSE
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USDA Economic Research Service, ERS
Report Number 34, December 2006.
Lloyd, S.E., J.M. Linehan, M. Desbruslais, S.
Joiner, J. Buckell, S. Brandner, J.D.
Wadsworth, and J. Collinge. (2004).
Characterization of two distinct prion
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encephalopathy transmissions to inbred
mice. J. of Gen Virology 85(8):2471–2478.
Manuelidis, L., Z.-X. Yu, N. Banquero, and B.
Mullins. (2007). Cells infected with scrapie
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05–03. The Office of Management and
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peer_review_agenda.shtml)
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Data Analysis. Pacific Grove, CA:
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Yamakawa, Y., K. Hagiwara, K. Nohtomi, Y.
Nakamura, M. Nishijima, Y. Higuchi, Y.
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List of Subjects
9 CFR Part 93
Animal diseases, Imports, Livestock,
Poultry and poultry products,
Quarantine, Reporting and
recordkeeping requirements.
9 CFR Part 94
Animal diseases, Imports, Livestock,
Meat and meat products, Milk, Poultry
and poultry products, Reporting and
recordkeeping requirements.
9 CFR Part 95
Animal feeds, Hay, Imports,
Livestock, Reporting and recordkeeping
requirements, Straw, Transportation.
9 CFR Part 96
Imports, Livestock, Reporting and
recordkeeping requirements.
I Accordingly, we are amending 9 CFR
parts 93, 94, 95, and 96 as follows:
PART 93—IMPORTATION OF CERTAIN
ANIMALS, BIRDS, AND POULTRY,
AND CERTAIN ANIMAL, BIRD, AND
POULTRY PRODUCTS;
REQUIREMENTS FOR MEANS OF
CONVEYANCE AND SHIPPING
CONTAINERS
1. The authority citation for part 93
continues to read as follows:
I
Authority: 7 U.S.C. 1622 and 8301–8317;
21 U.S.C. 136 and 136a; 31 U.S.C. 9701; 7
CFR 2.22, 2.80, and 371.4.
§ 93.405
[Amended]
2. In § 93.405, paragraph (a)(4) is
amended by removing the words
‘‘feedlot or recognized slaughtering
establishment’’ and adding in their
place the words ‘‘destination’’.
I 3. Section 93.419 is amended as
follows:
I a. Paragraphs (b) and (c) are revised to
read as set forth below.
I b. Paragraph (d) is redesignated as
paragraph (e).
I c. A new paragraph (d) is added to
read as set forth below.
I d. In newly redesignated paragraph
(e)(2), the reference to ‘‘paragraph
(d)(7)’’ is removed and a reference to
‘‘paragraph (e)(7)’’ is added in its place.
I
§ 93.419
Sheep and goats from Canada.
*
*
*
*
*
(b) If the sheep or goats are
unaccompanied by the certificate
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required by paragraph (a) of this section,
or if they are found upon inspection at
the port of entry to be affected with or
exposed to a communicable disease,
they shall be refused entry and shall be
handled or quarantined, or otherwise
disposed of, as the Administrator may
direct.
(c) Any sheep or goats imported from
Canada must not be pregnant, must be
less than 12 months of age when
imported into the United States and
when slaughtered, must be from a flock
or herd subject to a ruminant feed ban
equivalent to the requirements
established by the U.S. Food and Drug
Administration at 21 CFR 589.2000, and
must be individually identified by an
official Canadian Food Inspection
Agency eartag, applied before the
animal’s arrival at the port of entry into
the United States, that is determined by
the Administrator to meet standards
equivalent to those for official eartags in
the United States as defined in § 71.1 of
this chapter and to be traceable to the
premises of origin of the animal. No
person may alter, deface, remove, or
otherwise tamper with the individual
identification while the animal is in the
United States or moving into or through
the United States, except that the
identification may be removed at the
time of slaughter. The animals must be
accompanied by the certification issued
in accordance with § 93.405 that states,
in addition to the statements required
by § 93.405, that the conditions of this
paragraph have been met. Additionally,
for sheep and goats imported for
immediate slaughter, the certificate
must state that the conditions of
paragraphs (d)(1) through (d)(3) of this
section have been met, and, for sheep
and goats imported for other than
immediate slaughter, the certificate
must state that the conditions of
paragraphs (e)(1) and (e)(2) of this
section have been met.
(d) Sheep and goats imported for
immediate slaughter. Sheep and goats
imported from Canada for immediate
slaughter must be imported only
through a port of entry listed in
§ 93.403(b) or as provided for in
§ 93.403(f) in a means of conveyance
sealed in Canada with seals of the
Canadian Government, and must be
moved directly as a group from the port
of entry to a recognized slaughtering
establishment for slaughter as a group.
The sheep and goats shall be inspected
at the port of entry and otherwise
handled in accordance with § 93.408.
The seals on the means of conveyance
must be broken only at the port of entry
by the APHIS port veterinarian or at the
recognized slaughtering establishment
by an authorized USDA representative.
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If the seals are broken by the APHIS port
veterinarian at the port of entry, the
means of conveyance must be resealed
with seals of the U.S. Government
before being moved to the recognized
slaughtering establishment. The
shipment must be accompanied from
the port of entry to the recognized
slaughtering establishment by APHIS
Form VS 17–33, which must include the
location of the recognized slaughtering
establishment. Additionally, the sheep
and goats must meet the following
conditions:
(1) The animals have not tested
positive for and are not suspect for a
transmissible spongiform
encephalopathy;
(2) The animals have not resided in a
flock or herd that has been diagnosed
with BSE; and
(3) The animals’ movement is not
restricted within Canada as a result of
exposure to a transmissible spongiform
encephalopathy.
*
*
*
*
*
I 4. Section 93.420 is revised to read as
follows:
§ 93.420 Ruminants from Canada for
immediate slaughter other than bovines,
sheep, and goats.
The requirements for the importation
of sheep and goats from Canada for
immediate slaughter are contained in
§ 93.419. The requirements for the
importation of bovines from Canada for
immediate slaughter are contained in
§ 93.436. All other ruminants imported
from Canada for immediate slaughter, in
addition to meeting all other applicable
requirements of this part, must be
imported only through a port of entry
listed in § 93.403(b) or as provided for
in § 93.403(f) to a recognized
slaughtering establishment for slaughter,
in conveyances that must be sealed with
seals of the U.S. Government at the port
of entry. The seals may be broken only
at a recognized slaughtering
establishment in the United States by an
authorized USDA representative. The
shipment must be accompanied from
the port of entry to the recognized
slaughtering establishment by APHIS
Form VS 17–33, which must include the
location of the recognized slaughtering
establishment. Such ruminants shall be
inspected at the port of entry and
otherwise handled in accordance with
§ 93.408.
(Approved by the Office of Management and
Budget under control number 0579–0277)
5. Section 93.436 is amended as
follows:
I a. Paragraphs (a) and (b) are revised to
read as set forth below.
I
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b. In paragraph (c), the reference to
‘‘§§ 93.419(c) and 93.420’’ is removed
and a reference to ‘‘§§ 93.405 and
93.419’’ is added in its place.
I
§ 93.436 Ruminants from regions of
minimal risk for BSE.
*
*
*
*
*
(a) Bovines for immediate slaughter.
Bovines from a region listed in
§ 94.18(a)(3) of this subchapter may be
imported for immediate slaughter under
the following conditions:
(1) The bovines must have been born
on or after a date determined by APHIS
to be the date of effective enforcement
of a ruminant-to-ruminant feed ban in
the region of export. For bovines
imported from Canada, that date is
March 1, 1999.
(2) Each bovine must be individually
identified by an official eartag of the
country of origin, applied before the
animal’s arrival at the port of entry into
the United States, that is determined by
the Administrator to meet standards
equivalent to those for official eartags in
this chapter and to be traceable to the
premises of origin of the animal. No
person may alter, deface, remove, or
otherwise tamper with the official
identification while the animal is in the
United States or moving into or through
the United States, except that the
identification may be removed at the
time of slaughter;
(3) The bovines must be accompanied
by a certificate issued in accordance
with § 93.405 that states, in addition to
the statements required by § 93.405, that
the conditions of paragraphs (a)(1) and
(a)(2) of this section have been met;
(4) The bovines must be imported
only through a port of entry listed in
§ 93.403(b) or as provided for in
§ 93.403(f). The bovines shall be
inspected at the port of entry and
otherwise handled in accordance with
§ 93.408;
(5) The bovines must be moved
directly from the port of entry to a
recognized slaughtering establishment.
Bovines imported from Canada must be
moved to the slaughtering establishment
in conveyances that are sealed with
seals of the U.S. Government at the port
of entry. The seals may be broken only
at the recognized slaughtering
establishment by an authorized USDA
representative; and
(6) The bovines must be accompanied
from the port of entry to the recognized
slaughtering establishment by APHIS
Form VS 17–33.
(b) Bovines for other than immediate
slaughter. Bovines from a region listed
in § 94.18(a)(3) of this subchapter may
be imported for other than immediate
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slaughter under the following
conditions:
(1) The bovines must have been born
on or after a date determined by APHIS
to be the date of effective enforcement
of a ruminant-to-ruminant feed ban in
the region of export. For bovines
imported from Canada, that date is
March 1, 1999.
(2) The bovines must be permanently
and humanely identified before arrival
at the port of entry with a distinct and
legible mark identifying the exporting
country. Acceptable means of
permanent identification include the
following:
(i) A mark properly applied with a
freeze brand, hot iron, or other method,
and easily visible on the live animal and
on the carcass before skinning. Such a
mark must be not less than 2 inches nor
more than 3 inches high, and must be
applied to each animal’s right hip, high
on the tail-head (over the junction of the
sacral and first cocygeal vertebrae).
Bovines exported from Canada so
marked must be marked with ‘‘C∧N’’;
(ii) A tattoo with letters identifying
the exporting country must be applied
to the inside of one ear of the animal.
For bovines exported from Canada, the
tattoo must read ‘‘CAN’’;
(iii) Other means of permanent
identification upon request if deemed
adequate by the Administrator to
humanely identify the animal in a
distinct and legible way as having been
imported from the BSE minimal-risk
exporting region.
(3) Each bovine must be individually
identified by an official eartag of the
country of origin, applied before the
animal’s arrival at the port of entry into
the United States, that is determined by
the Administrator to meet standards
equivalent to those for official eartags in
§ 71.1 of this chapter and to be traceable
to the premises of origin of the animal.
No person may alter, deface, remove, or
otherwise tamper with the official
identification while the animal is in the
United States or moving into or through
the United States, except that the
identification may be removed at the
time of slaughter;
(4) The bovines must be accompanied
by a certificate issued in accordance
with § 93.405 that states, in addition to
the statements required by § 93.405, that
the conditions of paragraphs (a)(1) and
(a)(2) of this section have been met; and
(5) The bovines must be imported
only through a port of entry listed in
§ 93.403(b) or as provided for in
§ 93.403(f).
*
*
*
*
*
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I
removed and the words ‘‘paragraphs
(i)(1) through (i)(3)’’ are added in their
place, and the words ‘‘paragraphs (h)(1)
through (h)(4)’’ are removed and the
words ‘‘paragraphs (i)(1) through (i)(4)’’
are added in their place.
I k. In newly redesignated paragraph
(i)(4)(iii), the reference to ‘‘paragraph
(h)(2)’’ is removed and a reference to
‘‘paragraph (i)(1)’’ is added in its place.
Authority: 7 U.S.C. 450, 7701–7772, 7781–
7786, and 8301–8317; 21 U.S.C. 136 and
136a; 31 U.S.C. 9701; 7 CFR 2.22, 2.80, and
371.4.
§ 95.4 Restrictions on the importation of
processed animal protein, offal, tankage,
fat, glands, certain tallow other than tallow
derivatives, and blood and blood products
due to bovine spongiform encephalopathy.
PART 94—RINDERPEST, FOOT-ANDMOUTH DISEASE, FOWL PEST (FOWL
PLAGUE), EXOTIC NEWCASTLE
DISEASE, AFRICAN SWINE FEVER,
CLASSICAL SWINE FEVER, AND
BOVINE SPONGIFORM
ENCEPHALOPATHY: PROHIBITED
AND RESTRICTED IMPORTATIONS
6. The authority citation for part 94
continues to read as follows:
§ 94.19
[Amended]
7. Section 94.19 is amended as
follows:
I a. By removing the words ‘‘and small
intestine’’ each time they appear in
paragraphs (a)(2), (b)(2), and (f).
I b. By removing the Note to paragraph
(a).
I c. By removing the Note to paragraph
(b).
I d. By removing the Note to paragraph
(f).
I
PART 95—SANITARY CONTROL OF
ANIMAL BYPRODUCTS (EXCEPT
CASINGS), AND HAY AND STRAW,
OFFERED FOR ENTRY INTO THE
UNITED STATES
8. The authority citation for part 95
continues to read as follows:
I
Authority: 7 U.S.C. 8301–8317; 21 U.S.C.
136 and 136a; 31 U.S.C. 9701; 7 CFR 2.22,
2.80, and 371.4.
9. Section 95.4 is amended as follows:
a. The section heading and paragraph
(a) introductory text are revised to read
as set forth below.
I b. Paragraphs (a)(1)(ii) and (a)(1)(iv)
are revised to read as set forth below.
I c. In paragraph (b), the words
‘‘paragraphs (d) and (h)’’ are removed
and the words ‘‘paragraphs (d), (e), and
(i)’’ are added in their place.
I d. Paragraph (d) introductory text is
revised to read as set forth below.
I e. The ‘‘Note to paragraph (f)’’ and the
‘‘Note to paragraph (g)’’ are removed.
I f. Paragraphs (e) through (h) are
redesignated as paragraphs (f) through
(i), respectively.
I g. The ‘‘Note’’ currently following
newly redesignated paragraph (f) is
redesignated as ‘‘Note to paragraph (f)’’.
I h. New paragraph (e) is added to read
as set forth below.
I i. In newly redesignated paragraph
(h)(1)(i), the words ‘‘and small
intestine’’ are removed.
I j. In newly redesignated paragraph (i)
introductory text, the words
‘‘paragraphs (h)(1) through (h)(3)’’ are
I
I
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(a) Except as provided in paragraphs
(c) through (i) of this section, the
importation of the following is
prohibited:
(1) * * *
(ii) Glands, unprocessed fat tissue,
and blood and blood products derived
from ruminants;
*
*
*
*
*
(iv) Derivatives of glands and blood
and blood products derived from
ruminants.
*
*
*
*
*
(d) Except as provided in paragraph
(e) of this section, the importation of
serum albumin, serocolostrum, amniotic
liquids or extracts, and placental liquids
derived from ruminants that have been
in any region listed in § 94.18(a) of this
chapter, and collagen and collagen
products that meet any of the conditions
listed in paragraphs (a)(1) through (a)(3)
of this section, is prohibited unless the
following conditions have been met:
*
*
*
*
*
(e) Bovine blood and blood products
that are otherwise prohibited
importation under paragraph (a)(1) or
(d) of this section may be imported into
the United States if they meet the
following conditions:
(1) For blood collected at slaughter
and for products derived from blood
collected at slaughter:
(i) The blood was collected in a closed
system in which the blood was
conveyed directly from the animal in a
closed conduit to a closed receptacle, or
was collected otherwise in a hygienic
manner that prevents contamination of
the blood with SRMs.
(ii) The slaughtered animal passed
ante-mortem inspection and was not
subjected to a pithing process or to a
stunning process with a device injecting
compressed air or gas into the cranial
cavity;
(2) For fetal bovine serum:
(i) The blood from which the fetal
bovine serum was derived was collected
in a closed system in which the blood
was conveyed directly from the animal
in a closed conduit to a closed
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Federal Register / Vol. 72, No. 180 / Tuesday, September 18, 2007 / Rules and Regulations
receptacle, or was collected otherwise in
a hygienic manner that prevents
contamination of the blood with SRMs;
(ii) The dam of the fetal calf passed
ante-mortem inspection and was not
subjected to a pithing process or to a
stunning process with a device injecting
compressed air or gas into the cranial
cavity;
(iii) The uterus was removed from the
dam’s abdominal cavity intact and taken
to a separate area sufficiently removed
from the slaughtering area of the facility
to ensure that the fetal blood was not
contaminated with SRMs when
collected.
(3) For blood collected from live
donor bovines and for products derived
from blood collected from live donor
bovines:
(i) The blood was collected in a closed
system in which the blood was
conveyed directly from the animal in a
closed conduit to a closed receptacle, or
was collected otherwise in a hygienic
manner that prevents contamination of
the blood with SRMs;
(ii) The donor animal was free of
clinical signs of disease.
(4) Each shipment to the United States
is accompanied by an original certificate
signed by a full-time salaried veterinary
officer of the national government of the
region of origin, or issued by a
veterinarian designated by or accredited
by the national government of the region
of origin, representing that the
veterinarian issuing the certificate was
authorized to do so. The certificate must
state that the requirements of paragraph
(e)(1), (e)(2), or (e)(3) of this section, as
applicable, have been met.
*
*
*
*
*
PART 96—RESTRICTION OF
IMPORTATIONS OF FOREIGN ANIMAL
CASINGS OFFERED FOR ENTRY INTO
THE UNITED STATES
10. The authority citation for part 96
continues to read as follows:
pwalker on PROD1PC71 with RULES2
I
VerDate Aug<31>2005
19:35 Sep 17, 2007
Jkt 211001
Authority: 7 U.S.C. 8301–8317; 21 U.S.C.
136 and 136a; 7 CFR 2.22, 2.80, and 371.4.
11. In § 96.1, definitions of Food and
Drug Administration and Food Safety
and Inspection Service are added, in
alphabetical order, to read as follows:
I
§ 96.1
Definitions.
*
*
*
*
*
Food and Drug Administration. The
Food and Drug Administration of the
United States Department of Health and
Human Services.
Food Safety and Inspection Service.
The Food Safety and Inspection Service
of the United States Department of
Agriculture.
*
*
*
*
*
12. In § 96.2, paragraph (b) is revised
to read as follows:
I
§ 96.2 Prohibition of casings due to
African swine fever and bovine spongiform
encephalopathy.
*
*
*
*
*
(b) Ruminant casings. The
importation of casings, except stomachs,
from ruminants that originated in or
were processed in any region listed in
§ 94.18(a) of this subchapter is
prohibited, except as provided in
paragraphs (b)(1) and (b)(2) of this
section:
(1) Casings that are derived from
sheep that were slaughtered in a region
listed in § 94.18(a)(3) of this subchapter
at less than 12 months of age and that
were from a flock subject to a ruminant
feed ban equivalent to the requirements
established by the U.S. Food and Drug
Administration at 21 CFR 589.2000 may
be imported.
(2) Casings that are derived from
bovines that were slaughtered in a
region listed in § 94.18(a)(3) of this
subchapter may be imported, provided,
if the casings are derived from the small
intestine, the casings are derived from
that part of the small intestine that is
eligible for use as human food in
PO 00000
Frm 00067
Fmt 4701
Sfmt 4700
53379
accordance with the requirements
established by the Food Safety and
Inspection Service at 9 CFR 310.22 and
the Food and Drug Administration at 21
CFR 189.5.
(3) Casings imported in accordance
with either paragraph (b)(1) or (b)(2) of
this section must be accompanied by a
certificate that:
(i) States that the casings meet the
conditions of this section;
(ii) Is written in English;
(iii) Is signed by an individual eligible
to issue the certificate required under
§ 96.3; and
(iv) Is presented to an authorized
inspector at the port of entry.
*
*
*
*
*
13. In § 96.3, paragraph (d) is revised
to read as follows:
I
§ 96.3
Certificate for animal casings.
*
*
*
*
*
(d) In addition to meeting the
requirements of this section, the
certificate accompanying sheep casings
from a region listed in § 94.18(a)(3) of
this subchapter must state that the
casings meet the requirements of
§ 96.2(b)(1), and the certificate
accompanying bovine casings from a
region listed in § 94.18(a)(3) of this
subchapter must state that the casings
meet the requirements of § 96.2(b)(2).
*
*
*
*
*
Done in Washington, DC, this 12th day of
September 2007.
Charles D. Lambert,
Acting Under Secretary for Marketing and
Regulatory Programs.
[FR Doc. 07–4595 Filed 9–14–07; 8:45 am]
BILLING CODE 3410–34–P
E:\FR\FM\18SER2.SGM
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Agencies
[Federal Register Volume 72, Number 180 (Tuesday, September 18, 2007)]
[Rules and Regulations]
[Pages 53314-53379]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 07-4595]
[[Page 53313]]
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Part III
Department of Agriculture
-----------------------------------------------------------------------
Animal and Plant Health Inspection Service
-----------------------------------------------------------------------
9 CFR Parts 93, 94, 95, and 96
Bovine Spongiform Encephalopathy; Minimal-Risk Regions; Importation of
Live Bovines and Products Derived From Bovines; Final Rule
Federal Register / Vol. 72, No. 180 / Tuesday, September 18, 2007 /
Rules and Regulations
[[Page 53314]]
-----------------------------------------------------------------------
DEPARTMENT OF AGRICULTURE
Animal and Plant Health Inspection Service
9 CFR Parts 93, 94, 95, and 96
[Docket No. APHIS-2006-0041]
RIN 0579-AC01
Bovine Spongiform Encephalopathy; Minimal-Risk Regions;
Importation of Live Bovines and Products Derived From Bovines
AGENCY: Animal and Plant Health Inspection Service, USDA.
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: We are amending the regulations regarding the importation of
animals and animal products to establish conditions for the importation
of the following commodities from regions that present a minimal risk
of introducing bovine spongiform encephalopathy into the United States:
Live bovines for any use born on or after a date determined by the
Animal and Plant Health Inspection Service to be the date of effective
enforcement of a ruminant-to-ruminant feed ban in the region of export;
blood and blood products derived from bovines; and casings and part of
the small intestine derived from bovines. We are making these
amendments after conducting a risk assessment and comprehensive
evaluation of the issues and concluding that such bovines and bovine
products can be safely imported under the conditions described in this
rule. This document also removes the delay in applicability of certain
provisions of a final rule published in January 2005.
DATES: Effective Date: November 19, 2007.
FOR FURTHER INFORMATION CONTACT: For information regarding ruminant
products, contact Dr. Karen James-Preston, Director, Technical Trade
Services, Animal Products, National Center for Import and Export, VS,
APHIS, 4700 River Road Unit 38, Riverdale, MD 20737-1231; (301) 734-
4356.
For information concerning live ruminants, contact Dr. Lee Ann
Thomas, Director, Technical Trade Services, Animals, Organisms and
Vectors, and Select Agents, National Center for Import and Export, VS,
APHIS, 4700 River Road Unit 38, Riverdale, MD 20737-1231; (301) 734-
4935.
For other information concerning this proposed rule, contact Dr.
Lisa Ferguson, Senior Staff Veterinarian, National Center for Animal
Health Programs, VS, APHIS, 4700 River Road Unit 43, Riverdale, MD
20737-1231; (301) 734-6954.
SUPPLEMENTARY INFORMATION:
Purpose
This document makes final a proposed rule that the Animal and Plant
Health Inspection Service (APHIS) of the U.S. Department of Agriculture
(USDA or the Department) published in the Federal Register on January
9, 2007 (72 FR 1101-1129, Docket No. APHIS-2006-0041). Additionally, it
removes the delay of applicability of certain provisions of a final
rule APHIS published in January 2005. The removal of delay is discussed
below under the heading ``Removal of Partial Delay of Applicability of
Provisions of January 2005 Final Rule.''
In our January 2007 proposed rule, we proposed to amend the
regulations in 9 CFR parts 93, 94, 95, and 96 to establish conditions
for the importation of the following commodities from regions that
present a minimal risk of introducing bovine spongiform encephalopathy
(BSE) into the United States: Live bovines for any use born on or after
a date determined by APHIS to be the date of effective enforcement of a
ruminant-to-ruminant feed ban in the region of export; blood and blood
products derived from bovines; and casings and part of the small
intestine derived from bovines.
In this document, we respond to public comments received on the
proposed rule and its underlying risk assessment and other supporting
analyses. Additionally, we discuss below the history of APHIS
rulemaking related to BSE minimal-risk regions.
Background
APHIS regulates the importation of animals and animal products into
the United States to guard against the introduction of animal diseases.
The regulations in 9 CFR parts 93, 94, 95, and 96 (referred to below as
the regulations) govern the importation of certain animals, birds,
poultry, meat, other animal products and byproducts, hay, and straw
into the United States in order to prevent the introduction of various
animal diseases, including BSE, a chronic degenerative disease
affecting the central nervous system of cattle.
With some exceptions, APHIS' regulations prohibit or restrict the
importation of live ruminants and certain ruminant products and
byproducts from the following three categories of regions with regard
to BSE: (1) Those regions in which BSE is known to exist (listed in
Sec. 94.18(a)(1) of the regulations); (2) those regions that present
an undue risk of introducing BSE into the United States because their
import requirements are less restrictive than those that would be
acceptable for import into the United States and/or because the regions
have inadequate surveillance (listed in Sec. 94.18(a)(2) of the
regulations); and (3) those regions that present a minimal risk of
introducing BSE into the United States via live ruminants and ruminant
products and byproducts (listed in Sec. 94.18(a)(3) of the
regulations).
Chronology of Federal Register Publications Regarding BSE Minimal-Risk
Regions
We added the Sec. 94.18(a)(3) category (BSE minimal-risk regions)
to the regulations in a final rule published in the Federal Register on
January 4, 2005 (70 FR 459-553, Docket No. 03-080-3). In the final
rule, we specified which commodities may be imported from BSE minimal-
risk regions and under what conditions, and recognized Canada as a BSE
minimal-risk region. (At this time, Canada is the only recognized BSE
minimal-risk region.)
The January 2005 final rule was based on a proposed rule we
published in the Federal Register on November 4, 2003 (68 FR 62386-
62405, Docket No. 03-080-1). On December 25, 2003, less than 2 weeks
before the close of the comment period for our proposed rule, a case of
BSE in a dairy cow of Canadian origin in Washington State was verified
by an international reference laboratory.
In response to comments from the public requesting an extension of
the comment period and in order to give the public an additional
opportunity to comment on the proposed rule in light of this
development, on March 8, 2004, we published a document in the Federal
Register (69 FR 10633-10636, Docket No. 03-080-2) reopening the comment
period.
On January 4, 2005, along with the final rule, we published in the
Federal Register a notice (70 FR 554, Docket No. 03-080-4) announcing
the availability of, and requesting comments on, a final environmental
assessment (EA) regarding the potential impact on the quality of the
human environment due to the importation of ruminants and ruminant
products and byproducts from Canada under the conditions specified in
the final rule. On January 21, 2005, we published in the Federal
Register a notice (70 FR 3183-3184, Docket No. 03-080-5) announcing the
availability of a corrected version of the EA for public review and
comment. On April 8, 2005, we published in the Federal Register a
finding (70 FR 18252-18262, Docket No. 03-080-7) that the provisions of
the final rule would not
[[Page 53315]]
have a significant impact on the quality of the human environment.
On March 11, 2005, we published a document in the Federal Register
that gave notice that the Secretary of Agriculture was delaying until
further notice the implementation of certain provisions of the final
rule with regard to certain commodities (70 FR 12112-12113, Docket No.
03-080-6).
On November 28, 2005, we published in the Federal Register an
interim rule (70 FR 71213-71218, Docket No. 03-080-8) that amended
certain provisions established by the January 2005 final rule. The
interim rule broadened the list of who is authorized to break seals on
conveyances and allows transloading under supervision of products
transiting the United States.
On March 14, 2006, we published in the Federal Register a technical
amendment (71 FR 12994-12998, Docket No. 03-080-9) that clarified our
intent with regard to certain provisions in the January 2005 final rule
and corrected several inconsistencies within the rule.
On August 9, 2006, we published in the Federal Register a proposed
rule (71 FR 45439-45444, Docket No. APHIS-2006-0026) that proposed to
amend the provisions established by the January 2005 final rule by
removing several restrictions regarding the identification of animals
and the processing of ruminant materials from BSE minimal-risk regions,
and by relieving BSE-based restrictions on hide-derived gelatin from
BSE minimal-risk regions. We solicited comments concerning our proposal
for 60 days ending October 10, 2006. On November 9, 2006, we published
a document in the Federal Register (71 FR 65758-65759, Docket No.
APHIS-2006-0026) reopening and extended the comment period until
November 24, 2006. We received a total of 10 comments by that date. We
are considering the issues raised by the commenters and will address
them in a separate rulemaking document.
Scope of the January 2005 Final Rule
The regulations established by the January 2005 final rule and
subsequent amendments have allowed the importation from BSE minimal-
risk regions of live bovines that are under 30 months of age when
imported and when slaughtered and that have been subject to a ruminant
feed ban equivalent to that in place in the United States.
We did not attempt, for that rulemaking, to assess the BSE risk
associated with the importation of live bovines 30 months of age or
older from a BSE minimal-risk region. Our March 8, 2004, document that
reopened the comment period on the November 2003 proposed rule stated
that APHIS was evaluating the appropriate approach with regard to the
importation of live animals 30 months of age or older from BSE minimal-
risk regions, and would address that issue in a supplemental rulemaking
proposal in the Federal Register. The provisions in our January 9,
2007, proposed rule regarding live bovines were the result of that
evaluation.
The regulations established by the January 2005 final rule also
provided for the importation of the following commodities derived from
bovines of any age: (1) Meat, meat food products, and meat byproducts;
(2) whole or half carcasses; (3) offal; (4) tallow composed of less
than 0.15 percent insoluble impurities that are not otherwise eligible
for importation under Sec. 95.4(a)(1)(i) of the regulations; and (5)
gelatin derived from bones of bovines that is not otherwise eligible
for importation under Sec. 94.18(c) of the regulations.
The January 2005 final rule and subsequent amendments did not
change the regulations concerning the importation of blood and blood
products from regions listed in Sec. 94.18(a); the requirements for
the importation of blood and blood products from BSE minimal-risk
regions remain the same as the requirements for importation of blood
and blood products from other regions listed in Sec. 94.18(a)--only
serum and serum albumin have been eligible for importation. The January
2005 final rule also did not change the regulations concerning the
importation of bovine casings (defined as intestines, stomachs,
esophagi, and urinary bladders) from regions listed in Sec. 94.18(a);
the requirements for the importation of bovine casings from BSE
minimal-risk regions remain the same as the requirements for
importation of bovine casings from other regions listed in Sec.
94.18(a)--only bovine stomachs are eligible for importation.
The January 2005 final rule and subsequent amendments allowed trade
to resume in many, but not all, of the commodities that had been
prohibited importation from Canada following detection of a BSE-
infected cow in Canada in May 2003. Following our January 2005 final
rule, we continued to consider the BSE risk associated with older
bovines and other bovine products from BSE minimal-risk regions--and
Canada in particular--including bovine blood and blood products, bovine
small intestine other than the distal ileum, and bovine casings, and
included provisions in our January 2007 proposed rule for the
importation of those commodities.\1\
---------------------------------------------------------------------------
\1\ The regulations regarding BSE minimal-risk regions apply to
bison as well as cattle. In Sec. Sec. 93.400, 94.0, and 95.1 of the
regulations, bovine is defined as Bos taurus, Bos indicus, and Bison
bison. Although the research and other data cited in this rulemaking
refer to bovines other than bison (i.e., to ``cattle''), there is no
evidence to indicate that the BSE susceptibility of bison differs
from that of cattle. We therefore assume that our conclusions based
on cattle-specific evidence discussed in this rulemaking are also
applicable to bison. Given that no cases of BSE have been detected
in bison, this is likely a conservative assumption. The provisions
of this rule apply to bovines as defined in the regulations, which
include bison.
---------------------------------------------------------------------------
Peer Review of APHIS' Risk Assessment
As part of this rulemaking, APHIS conducted an assessment that
evaluated the animal health risk to the United States of BSE--i.e., the
likelihood of establishment and the potential impacts of cases that may
occur even without establishment--as a result of importing the bovine
commodities considered in this rule (APHIS 2006b). Our assessment
concluded that, over the 20 years of the analysis, the BSE risk to the
United States is negligible. We made the risk assessment available for
public review and comment at the time the proposed rule was published.
In addition to making the risk assessment available for review and
comment by the general public, we requested an external, formal,
independent peer review of the assessment by recognized experts in the
field, consistent with guidelines of the U.S. Office of Management and
Budget (OMB 2004). The objective of the peer review was to determine
whether the risk assessment was scientifically sound, transparent, and
consistent with international standards (e.g., those by the OIE); the
application of external assessments or models was appropriate; and the
assumptions were justified, supported and reasonable. Comments
submitted by the public on the proposed rule were submitted to the peer
reviewers for their consideration. The peer review process was
coordinated by an independent private contractor.
The full peer review report may be viewed at https://
www.aphis.usda.gov/peer_review/peer_review_agenda.shtml.
Additionally, we have included below, under the heading ``Final Report
from Peer Review of APHIS' Risk Assessment and Responses to Peer
Reviewer Questions and Recommendations,'' APHIS' responses to reviewer
comments that we consider representative of the content-related
questions and recommendations of the report, and our response to those
questions and recommendations. In summary, the
[[Page 53316]]
reviewers found that the methods used in the risk assessment were
scientifically rigorous in terms of using existing literature and
models appropriately and making sound assumptions and that the risk
assessment itself adhered to international risk assessment standards.
The reviewers also agreed with the conclusion that the likelihood of
establishment of BSE in the U.S. cattle population is negligible.
In addition to being supportive of the methods, evidence, and
conclusions presented by APHIS in the risk assessment, the reviewers
made several useful suggestions for its improvement. We made several
clarifications and updates in consideration of these comments. While we
expect that the changes improve the transparency and accuracy of the
document, they do not alter our conclusion that the risk to the United
States of BSE--i.e., the likelihood of establishment and the potential
impacts of cases that may occur even without establishment--resulting
from the changes outlined in the proposed rule is negligible.
Removal of Partial Delay of Applicability of Provisions of January 2005
Final Rule
Our January 2005 final rule made eligible for importation from
Canada meat that is derived from bovines slaughtered in BSE minimal-
risk regions, as well as certain other specified commodities derived
from such bovines, provided certain specified risk-mitigating
conditions have been met. The risk analysis we conducted for that
rulemaking indicated a low BSE risk from such commodities derived from
bovines of any age if certain conditions are met (APHIS 2004). These
conditions include the removal of those tissues considered at
particular risk of containing the BSE agent in infected animals
(specified risk materials, or SRMs). In that rulemaking, we discussed
regulatory requirements implemented by FSIS in 2004 that banned SRMs
from the human food supply in the United States, and we stated that the
Canadian Government had established similar safeguards in Canada.
Consequently, we provided that meat, meat byproducts, meat food
products, and offal derived from bovines are eligible for importation
from BSE minimal-risk regions if the following conditions, as well as
all other applicable requirements of the regulations, are met:
The commodity is derived from bovines that have been
subject to a ruminant feed ban equivalent to the requirements
established by the U.S. Food and Drug Administration at 21 CFR
589.2000;
The commodity is derived from bovines for which an air-
injected stunning process was not used at slaughter; and
The SRMs and small intestine of the bovines from which the
commodity was derived were removed at slaughter.
Additionally we provided that tallow composed of less than 0.15
percent insoluble impurities that is not otherwise eligible for
importation under 9 CFR 95.4(a)(1)(i), and gelatin derived from bones
of bovines that is not otherwise eligible for importation under 9 CFR
94.18(c) are eligible for importation from BSE minimal-risk regions,
provided certain specified conditions are met.
In the economic analysis we conducted for the January 2005 final
rule, we evaluated the potential economic effects of implementing that
rulemaking, including implementation of the provisions allowing the
importation of meat and other commodities derived from bovines
slaughtered in BSE minimal-risk regions (APHIS 2004a).
In March 2005, APHIS published a document in the Federal Register
that, pursuant to an announcement by the Secretary of Agriculture on
February 9, 2005, delayed the applicability of the provisions in our
January 2005 final rule as they apply to the importation from Canada of
the following commodities when derived from bovines 30 months of age or
older when slaughtered: (1) Meat, meat food products, and meat
byproducts other than liver; (2) whole or half carcasses; (3) offal;
(4) tallow composed of less than 0.15 percent insoluble impurities that
is not otherwise eligible for importation under 9 CFR 95.4(a)(1)(i);
and (5) gelatin derived from bones of bovines that is not otherwise
eligible for importation under 9 CFR 94.18(c).
In his February 9, 2005, announcement, the Secretary stated that
because ongoing investigations into recent finds of BSE in Canada in
animals over 30 months of age were not complete, he felt it prudent to
delay the effective date for allowing imports of meat from bovines 30
months of age and over. He also indicated that the delay of
applicability would address concerns that the January 2005 final rule
allowed the importation of beef from bovines 30 months of age or older,
while continuing to prohibit the importation of live cattle 30 months
of age or older for processing in the United States. The Secretary
stated that the Department would consider and develop a plan--based on
the latest scientific information and with the protection of public and
animal health as the highest priority--to allow imports of live bovines
30 months of age or older as well as beef from animals 30 months of age
and older.
Since the date of the partial delay of applicability of our January
2005 final rule, we have obtained additional information regarding all
aspects of the issues that prompted the delay of applicability and have
conducted additional analyses in line with the plan as described. The
risk assessment for this final rule demonstrates the negligible BSE
risk from the importation of additional classes of live cattle,
including those 30 months of age or older. This includes acknowledging
the potential risk pathway that could be available if the SRMs from
infected imported cattle entered the ruminant feed supply in
contravention of current feed regulations. The negligible risk from the
importation of live older cattle therefore gives further support to the
conclusion of the risk analysis conducted for our January 2005 final
rule regarding meat and meat products derived from bovines of any age
in BSE minimal-risk regions. Specifically, the risk is even lower for
the importation of meat and meat products, as the SRMs will be removed
in accordance with the regulations, than for live bovines.
Therefore, this document will remove the partial delay of
applicability of the January 2005 final rule. The removal of the
partial delay of applicability will become effective on the date that
the other provisions of this document become applicable. Including the
removal of the partial delay of applicability in this final rule and
making it effective along with the other provisions of this rule will
enable APHIS to more efficiently communicate the necessary
implementation instructions to U.S. Customs and Border Protection and
to APHIS field personnel. Additionally, it will provide commercial
entities more flexibility in carrying out import planning based on the
relative economic merits of importing live bovines or meat and other
products derived from bovines.
Because, for reasons of efficiency for APHIS and the regulated
community, the Secretary has decided to remove the delay in
applicability as part of this document, we looked at the economic
effects of doing so in combination with allowing the importation of
bovines born on or after March 1, 1999. Although we previously analyzed
the economic effects of allowing the importation of meat and other
products derived from bovines 30 months of age
[[Page 53317]]
or older, the economic analysis for this rule provides an updated
analysis.
Public Comments on the January 2007 Proposed Rule
We solicited comments concerning our January 2007 proposal for 60
days ending March 12, 2007. We received close to 400 comments by that
date. The commenters included cattle industry and farm bureau
associations, consumer groups, representatives of the Canadian
Government and other foreign countries, State Departments of
Agriculture, food processing companies, individual cattle producers,
and other members of the public.
Subjects of Comments Received
A number of commenters supported the rule and recommended no
changes to the proposed provisions. Other commenters supported the rule
in general but recommended certain changes or actions. Other comments
consisted only of recommended changes, objections to the rule in
general or to specific provisions, or requests for clarification. We
discuss below by topic the issues raised by commenters and our response
to those comments.
General Opposition to Imports
Issue: A number of commenters expressed general opposition to the
importation of any bovines or bovine products from BSE minimal-risk
regions.
Response: It appears to us that these commenters are not addressing
just our January 2007 proposed rule, but, rather, also the January 2005
final rule that recognized the category of BSE minimal-risk regions and
established conditions for the importation of certain ruminants and
ruminant products from such regions.
As we discussed in the January 2005 final rule, the comprehensive
analysis and evaluation we conducted for that rulemaking led to the
conclusion that the conditions specified in that rule for the
importation of ruminants and ruminant products from BSE minimal-risk
regions would be effective and would therefore protect against the
introduction of BSE into the United States. Our January 2007 proposed
rule considered expansion of the types of commodities allowed
importation from BSE minimal-risk regions, based on an evaluation of
the risk (i.e., the likelihood of establishment and the potential
impacts of cases that may occur even without establishment) of
importing from Canada live animals, blood and blood products, and the
small intestine excluding distal ileum.) Given the determination of
negligible BSE risk associated with the provisions of this final rule,
and the findings associated with our 2005 final rule, there is no
scientific basis for increasing restrictions from those already in
effect or being established in this rule.
Issue: A number of commenters expressed opposition, without further
explanation, to the importation from BSE minimal-risk regions of live
bovines 30 months of age or older and to the importation of products
derived from such bovines.
Response: We discussed in our January 2007 proposed rule the
rationale for our proposal to allow the importation, under certain
conditions, of live bovines 30 months or older from BSE minimal-risk
regions. We discussed further the assessment of the disease risk of
allowing such imports that we conducted before issuing our proposal. It
is not clear to us which factors in our risk assessment or discussion
of rationale were being addressed by those commenters who expressed
general opposition to the importation of live bovines 30 months of age
or older. We continue to consider the BSE risk from importing live
bovines under the conditions specified in this rule to be negligible.
Issue: Several commenters who expressed opposition to the proposed
rule expressed concern that the agent that causes BSE has yet to be
fully characterized. The commenters stated that what we know about BSE
is mostly supposition, which should be a compelling reason not to allow
the importation of cattle from a region of known BSE outbreaks. One
commenter stated that research recently conducted at Yale University
suggests that one of the agents that activates BSE may be viral, which,
according to the commenter, implies that a feed ban is effective only
when the virus is not present or active.
Response: As one of the commenters noted, some researchers
(Manuelidis et al., 2007) suggest that diseases characterized as
transmissible spongiform encephalopathies (TSEs), such as BSE, may be
caused by viruses, although, at this point, no infection-specific
nucleic acids have been identified.
Experimental data and epidemiological studies strongly suggest that
contaminated feed containing ruminant proteins derived from infected
animals was the source of the epidemic, and that the epidemic was
perpetuated through the use of these materials in ruminant feed. APHIS
considers that regardless of the characteristics of the BSE causal
agent, it is clear that the epidemic was sustained and amplified by the
recycling of BSE infected cattle into cattle feed. Despite the
difficulty in definitively determining the causal agent of BSE, risk
factors for transmission of the agent have been identified. The
identification and characterization of these risk factors through
epidemiological and experimental study have allowed the development of
effective mitigations to prevent BSE spread. The development and
demonstrated effectiveness of those mitigations does not require
identification of the agent itself. We consider mitigation measures
that address the risk factors for BSE to be effective regardless of the
precise nature of the BSE agent.
Prevalence of BSE in Canada
Although the provisions of this rule apply to any region recognized
by APHIS as a BSE minimal-risk region, at present APHIS recognizes only
one country, Canada, as such a region. Therefore, in evaluating the BSE
risk of implementing this rule, we conducted an assessment of the risk
of importing bovines and bovine products from Canada under the
provisions of our proposed rule (APHIS 2006b). In our risk assessment,
we laid out the likely risk pathway (i.e., a series of occurrences or
steps necessary for disease to enter and become established).
In conducting our risk assessment, one of the factors we took into
account was the prevalence of BSE in Canada, since prevalence is one
factor that affects the likelihood of a BSE-infected bovine being
imported into the United States. We received a number of comments from
the public that addressed our estimate of the prevalence of BSE in
Canada. Although some of the comments supported our estimate of BSE
prevalence in Canada, in general the commenters maintained that such
prevalence is either higher than we estimated, may be increasing, or is
uncertain, or that our methods of estimating it were flawed. The
methodology we used to arrive at such estimates is discussed in detail
in our risk assessment. However, to provide some context for the issues
raised by commenters and discussed below, we summarize here the models
that we used in conducting our assessment.
The number of BSE cases detected through surveillance understates
the disease prevalence because exposed animals may be incubating
disease and carrying infectious material in their tissues without
presenting clinical symptoms. Like many transmissible spongiform
encephalopathies (TSEs),
[[Page 53318]]
BSE has an incubation period of several years. Therefore, the disease
is not detectable in its early stages with current technology.
Moreover, surveillance will miss a proportion of detectable cases.
Therefore, we applied statistical methods to the available
epidemiologic and surveillance data to estimate, with attendant
uncertainty, the prevalence of BSE in Canada.
We used two related, but distinct, methods to estimate BSE
prevalence in Canada: the BSurvE model and the Bayesian Birth Cohort
(BBC) model. Given its international prominence, we used the European
Union (EU) BSurvE model (Wilesmith et al., 2004, 2005), recently
developed for the purpose of estimating BSE prevalence in national
herds. The BSurvE model is noteworthy for its sound epidemiologic
structure, including stratifying cattle by age and cause of death
(i.e., healthy slaughter, fallen stock, casualty slaughter, or clinical
suspect) and accounting for the relative likelihood of detecting BSE in
various strata (EFSA 2004). The BSurvE model structure calculates BSE
surveillance point values (random sample size equivalents) represented
by targeted Canadian sampling of certain groups of cattle in which BSE
cases are more likely to be detected. This approach allows for the
inclusion of infected, but undetected, cases (such as young animals in
the early stages of incubation) in the estimate, which would be ignored
by conventional methods.
The other prevalence estimation model that we used is the BBC
model. This model uses the BSurvE model structure and incorporates
additional information. Unlike BSurvE, the BBC model adopts a Bayesian
statistical framework to incorporate prior information about the
decreased incidence of BSE observed in animals born after a feed ban
equivalent to the initial ruminant-to-ruminant feed ban introduced in
the United Kingdom in 1988.
Issue: One commenter stated that BSE has become ``firmly
established'' in Canada.
Response: We disagree with the comment, which we consider to
erroneously equate disease presence, which may be transient, with
disease establishment. In epidemiology, an infectious disease has
become established in a population when the disease is perpetuated in
the population without the need for reintroduction from an external
source. For example, OIE's sister agency, the international Commission
on Phytosanitary Measures (CPM) defines plant pest establishment as
``the perpetuation, for the foreseeable future, of a nonindigenous
biological agent within an area after entry'' (CPM 2001). With the
implementation and continuation of a feed ban in Canada, all evidence
points toward eventual eradication, rather than perpetuation of BSE in
that country.
Issue: One commenter stated that, since the time APHIS published
its January 2005 final rule classifying Canada as a BSE minimal-risk
region, the Agency has presented no new evidence that would support
allowing the importation from Canada of the additional commodities
discussed in the proposed rule. In fact, stated the commenter, evidence
points to Canada having a higher prevalence of BSE than APHIS had
previously determined.
Response: As discussed in our January 2007 proposed rule, we
revisited our earlier conclusions and policies by conducting a rigorous
risk assessment based on current available scientific knowledge of the
disease. We used peer reviewed risk assessment models in our analysis
to estimate the prevalence of the disease in Canada and to analyze the
likelihood of BSE establishment in the United States and the potential
impacts of cases that may occur even without establishment as a result
of the importation into the United States of the bovine commodities
considered in this rule. The risk assessment itself was peer reviewed
by experts in the field. As noted above, the reviewers agreed with the
conclusion that the risk of establishment of BSE in the U.S. cattle
population is negligible and noted that several assumptions in the risk
assessment actually over-estimate the risk, so the overall finding that
the BSE risk is negligible is reasonable. Based on the results of the
risk assessment, we concluded that we could safely import Canadian
cattle born on or after March 1, 1999, blood and blood products, and
small intestines, excluding the distal ileum.
Issue: Several commenters raised questions about the ability to
statistically determine BSE prevalence ``trends'' in Canada, but
reached different conclusions. Some commenters stated that the
trajectory of BSE prevalence in Canada cannot be determined by
available surveillance data and that, therefore, BSE prevalence in
Canada may be increasing. On the other hand, another commenter
requested that APHIS make clear that, despite the Agency's use of the
BSurvE Prevalence B estimate, prevalence should not be assumed constant
over time. The commenter requested that APHIS emphasize that lack of
statistical evidence that prevalence varies from cohort to cohort is
likely the result of inadequate statistical power,\2\ and that,
nevertheless, BSE prevalence in Canada is most likely decreasing.
---------------------------------------------------------------------------
\2\ The power of a statistical test is the probability of
rejecting the null hypothesis when it is false. The power depends on
the test level of significance, the magnitude of effect under the
alternative hypothesis, sample size, and variability in the
population. Rice (1988, pp.361-364) describes the calculation of
statistical power for comparing two independent samples.
---------------------------------------------------------------------------
Response: In our risk assessment for this rule, we acknowledge
that, given the rarity of BSE cases in Canada, the surveillance data
are unlikely to provide adequate statistical power to detect any trend.
However, as discussed in the risk assessment, we consider it likely
that the prevalence of BSE in Canada will decrease over time. With so
few total BSE cases observed in Canada, the statistical power to detect
differences in prevalence between cohorts is low. The peer reviewers of
our risk assessment concur with our conclusion. (RTI 2007, pp. 6-26, 6-
27).
Issue: One commenter estimated the Canadian BSE prevalence to be
6.4 cases per million cattle. Further, the commenter stated that this
prevalence estimate is smaller than the risk estimate provided by one
of APHIS' own risk assessments for a more pessimistic value of the
misfeeding rate. The commenter suggested that this discrepancy reflects
optimistic modeling assumptions in APHIS' risk assessment.
Response: We disagree with the commenter's analysis. Although the
commenter's alternative prevalence estimate, based on a simple
extrapolation method, falls within the 90 percent confidence interval
\3\ of APHIS' BSurvE Prevalence B estimate (2.4 to 6.8 cases per
million adult cattle) with an expected value of 3.9 per million case
per million adult cattle (APHIS 2006c, table 5), it is based on
different assumptions. Based on an analysis of BSE testing in the EU in
2001 and 2002, the commenter's prevalence estimate assumes that
targeted ``risk cattle'' are only 10 times more likely to test positive
for BSE than non-targeted routinely slaughtered cattle. Considering the
BSE testing conducted in the EU during 2001-2004 (EC 2005a, table 3, p.
23), cattle in the
[[Page 53319]]
European BSE risk animals category (emergency slaughter, clinical
suspects, and fallen stock) are 22 times more likely to test BSE
positive than cattle in the healthy slaughter category. Using the
commenter's simple extrapolation method and these more up-to-date data
on BSE test positive ratio, the resulting BSE prevalence estimate would
be 2.9 per million cattle. Although actually lower than the expected
value for the BSurvE estimate, this value also falls within the 90
percent confidence interval of the Agency's BSurvE Prevalence B
estimate, described above. APHIS calculated both the BSurvE Prevalence
B estimate and the Bayesian Birth Cohort (BBC) prevalence estimate, but
judged the latter to better characterize the BSE prevalence in Canada
over the next 20 years, due to the expected downward pressure exerted
on the disease by a feed ban.
---------------------------------------------------------------------------
\3\ A confidence interval is a statistical range with a
specified probability that a given parameter lies within the range.
For example, the 90 percent confidence interval of a distribution
indicates the range of values that we are 90 percent certain include
the parameter value of interest. It extends from the 5th percentile,
or 5 percent confidence level, at the low end of the distribution of
the 95th percentile, or 95 percent confidence level at the high end
of the distribution. Similarly, a 95 percent confidence interval
would extend from the2.5 percent confidence level to the 97.5
percent confidence level.
---------------------------------------------------------------------------
With regard to the commenter's suggestion of a discrepancy, the
commenter provides no specific reference to ``the risk estimate
provided by one of APHIS' own risk assessments,'' but appears to refer
to the main body of the 2005 report of Cohen and Gray (available at
https://www.fsis.usda.gov/PDF/BSE_Risk_Assess_Report_2005.pdf),
which was prepared for the USDA's Food Safety and Inspection Service
(FSIS). Cohen and Gray (2005) do not estimate Canadian BSE prevalence,
but rather the effect of introducing 500 BSE-infected cattle into the
United States, and the pessimistic misfeeding assumption estimates that
introduction would result in an expected 2,600 new cases over 20 years.
There is no discrepancy because this aspect of the Cohen and Gray 2005
report is not relevant to our estimate of Canadian BSE prevalence.
Issue: Based on APHIS'' statements that animals are infected within
their first year, and that feed produced prior to the feed ban would
not be available for longer than a year, one commenter stated that
additional undetected infected animals must have existed and been
rendered in order to provide infectivity to detected cases. Therefore,
stated the commenter, adding in these ``undetected'' animals raises the
number of Canada's known and measurable BSE cases rises from 10 to 14,
and APHIS' estimate of BSE prevalence in Canada based on 10 animals is
low.
Response: We disagree with the commenter's analysis and conclusion,
which assumes that we did not take into account the possibility of
undetected cases of BSE in arriving at our prevalence estimate. APHIS'
estimate of the prevalence of BSE in Canada was adjusted to account for
cases that would not be tested and for false negative test results.
Also, although the bulk of feed will be consumed within a year after it
is produced, residual infectivity may remain in the feed supply chain
for an extended period. For example, examination of BSE cases in
animals born in the United Kingdom after the 1996 ``reinforced feed
ban'' suggests that these animals may have been infected from the
persistence of the BSE agent in residual feed in storage bins (SEAC
2005).
Issue: One commenter suggested that it is likely that Canada has
numerous cattle over 30 months of age that are presently incubating the
BSE disease, rather than just a few (4.1) as suggested by APHIS.
Response: The estimate of 4.1 BSE-infected animals in the standing
Canadian adult cattle population was based on the expected BSE
prevalence in Canada under the BBC model. Using the estimated
prevalence under BSurvE Prevalence B resulted in an estimate of 23.2
BSE-infected animals in the standing Canadian adult cattle population.
Although, quantitatively, our risk assessment did not assume a decline
in BSE prevalence over the next 20 years, we qualitatively consider
such a decline to be likely because of continued compliance with the
feed ban. Therefore, in assessing the BSE risk associated with imports
from Canada over the next 20 years, we consider the result of the BBC
model to be the more applicable prevalence estimate for use in our
quantitative exposure model.
Issue: One commenter indicated that although it is unclear whether
the APHIS estimates of Canadian BSE prevalence included the BSE case
confirmed on August 23, 2006, the APHIS estimates certainly do not take
into account the case confirmed on February 7, 2007.
Response: We estimated Canadian BSE prevalence based on a 7-year
surveillance period through August 15, 2006. This surveillance period
included the detection of nine BSE cases of Canadian origin reported
through August 2006. Through surveillance conducted from August 16,
2006, through April 2007, Canada detected one BSE case born in 2000 and
another born in 2001 (CFIA 2007). The BSE prevalence estimation methods
used by APHIS (2006a) require detailed data to stratify tested cattle
by age and cause of death (healthy slaughter, fallen stock, casualty
slaughter, or clinical suspect) that are unavailable for the more
recent surveillance period. However, we can assess the sensitivity of
our previous Canadian BSE prevalence estimates by adding the two
additional cases without changing the BSE surveillance points
accumulated by Canada during the 7-year surveillance period through
August 15, 2006 (APHIS 2006a, table 4). \4\ This approach results in a
revised table of BSurvE points and BSE cases by birth year cohort that
reflects a total of 11 BSE cases of Canadian origin reported through
April 2007 (APHIS 2007, table i).
---------------------------------------------------------------------------
\4\ In the BsurveE model, specific ``point values'' are assigned
to each test sample, based on the surveillance stream or
subpopulation of animals from which it was collected, as well as the
likelihood of detecting infected cattle in that subpopulation. A
sample from the specific surveillance subpopulation where BSE is
most likely to be detected--i.e., a middle adult clinical suspect--
provides the most surveillance points. Conversely, a sample from the
subpopulation where BSE is least likely to be detected--generally
routine slaughter--provides the least points.
---------------------------------------------------------------------------
Using the same methods described in USDA's estimate of BSE
prevalence in Canada (APHIS 2006c), we obtain updated Canadian BSE
prevalence estimates:
BSurvE Prevalence B: 90 percent confidence interval = 3.0-
8.0 cases per million adult cattle
Bayesian Birth Cohort (BBC, Winbugs): 90 percent
confidence interval = 0.47-1.2 cases per million adult cattle
Because the updated confidence intervals contain the previous
expected value estimates of 0.68 per million (BBC) and 3.9 per million
(BSurvE Prevalence B) (APHIS 2006c), we conclude that the prevalence
estimate is not sensitive to the addition of the two additional BSE
cases discovered in Canada in August 2006 and February 2007.
Issue: One commenter stated that APHIS' expectation that the
prevalence of BSE in Canada will continue to decline from its present
minimal level does not acknowledge that the prevalence of BSE in Canada
right now is very uncertain. The commenter's independent estimate of
the current Canadian BSE prevalence is ``on the order of 4-6 per
million.''
Response: APHIS' risk assessment addresses the uncertainty in the
prevalence of BSE in Canada by considering estimates that differ by
more than a factor of five (APHIS 2006b). The BBC prevalence estimate
has an expected value of 0.68 cases per million adult cattle.\5\ The
BSurvE Prevalence B estimate has an expected value of 3.9 per million.
The
[[Page 53320]]
commenter's own method of estimation--``on the order of 4-6 per
million----provides an estimate on the same order of magnitude as the
BSurvE Prevalence B estimate of current prevalence. In either case,
prevalence is extremely low.
---------------------------------------------------------------------------
\5\ The BBC model provides a more precise estimate of BSE
prevalence in Canada by combining the epidemiologic theory and
application of surveillance data underlying the BSurvE model with
additional information about the effect of the feed ban on
prevalence.
---------------------------------------------------------------------------
Issue: One commenter stated that, although APHIS estimates that BSE
prevalence in Canada is about 6.8 or more times greater than in the
United States (0.68 vs. 0.1 per million), this does not adjust for the
important fact that the first BSE case in the United States was
imported from Canada.
Response: The APHIS October 2006 estimate of BSE prevalence in
Canada is based on the nine BSE cases of Canadian origin that had been
confirmed in North America as of August 23, 2006. This total includes a
case of BSE that was confirmed in Washington State on December 25, 2003
(APHIS 2006c, p. 1). The estimate of BSE prevalence in the United
States excludes this case.
Issue: One commenter stated that the calculation of BSE prevalence
in Canada used in APHIS' risk assessment excluded the European-born
case detected in 1993.
Response: The 1993 Canadian BSE case of European origin was likely
part of the original exogenous source of BSE infectivity introduced
into Canada that caused the subsequent generation of indigenous cases.
Imported cases of BSE reflect an exposure to the disease that occurred
elsewhere, and, therefore, are not generally included in estimates of
prevalence that reflect native exposure. Similarly, when APHIS
estimated the prevalence of BSE in the United States, the BSE-infected
cow of Canadian origin that was detected in Washington State in
December 2003 was excluded from the analysis, because it was an
imported animal. In addition, as noted in APHIS' estimation of BSE
prevalence in Canada (APHIS 2006c, p. 5), in accordance with OIE
guidelines (which indicate that surveillance points totals taken into
account in assessing a country's BSE risk be accumulated over a maximum
of 7 consecutive years), the estimated prevalence of BSE in Canada is
based on surveillance data accumulated over a 7-year period beginning
August 16, 1999. The 1993 case predates the OIE 7-year period.
Issue: One commenter indicated that APHIS should not take action on
the proposal until real surveillance data (not model-based predictions)
show that the BSE problem has abated. The commenter stated further that
denying Canada's BSE problem, or assuming it away with unvalidated and
incorrect risk modeling assumptions, does not responsibly manage BSE
risks to the United States.
Response: We disagree with the commenter. In low BSE prevalence
populations such as Canada, surveillance at levels that meet or even
greatly exceed OIE guidelines provide insufficient statistical power to
reliably detect changes in BSE prevalence over time. In other words,
starting with a very low number of infected animals makes it very
difficult to statistically demonstrate decreases in that number, even
when testing a relatively large number of animals.
The OIE Guidelines for BSE Surveillance (Type A) call for countries
to accumulate 300,000 BSE surveillance points over 7 consecutive years
in order to detect with 95 percent confidence a prevalence level of at
least one case of BSE per 100,000 animals (OIE 2006, Appendix 3.8.4).
To illustrate the comparative difficulty in demonstrating trends in
low versus high prevalence populations, consider two hypothetical
countries that have accumulated 1 million BSE surveillance points for
each of two cohorts: Animals born before and animals born after the
introduction of a ruminant-to-ruminant feed ban. Under this scenario,
sampling levels in both countries far exceed the OIE guidelines.
Assume, however, that the two countries differ with respect to their
initial prevalence--i.e., the initial prevalence in ``Country A'' is 1
infected animal per 10,000 animals, while that in ``Country B'' is 1
infected animal per 100,000 animals.
For a given surveillance level, the statistical power of a
hypothesis test can be evaluated as a function of the supposed change
in BSE prevalence between cohort 1 (pre-feed ban) and cohort 2 (post-
feed ban). The conventional minimum statistical power criterion is 80
percent. In other words, the probability that a statistical analysis
will detect a true difference across groups should be at least 80
percent. The conventional significance level is 5 percent, meaning that
we would conclude that a result was nonrandom if it were 5 percent or
less likely to occur by chance alone. In our hypothetical scenario, the
power of the surveillance in the country with higher prevalence,
Country A, to detect a 50 percent decline in BSE prevalence is 98
percent. In comparison, the power of the surveillance in the lower
prevalence Country B to detect a 50 percent decline in BSE prevalence
is only 25 percent. In other words, if the Country B feed ban actually
led to a 50 percent decline in BSE prevalence and the equivalent of 2
million random samples were collected (6.7 times the level under the
OIE guidelines), there would still be a 75 percent chance of concluding
that the prevalence was unchanged from its initial level of 1 infected
animal per 100,000 animals.
An important implication of the low statistical power of sampling
in low prevalence populations is that BSE surveillance data are
unlikely to provide a purely statistical basis for making a
determination about the date when a specific intervention (e.g., a
ruminant-to-ruminant feed ban) becomes effective, even when large
amounts of surveillance data are available. For example, according to
the OIE (2007a), the annual incidence of reported BSE cases in the
Netherlands dropped from 13.2 to 0.8 per million adult cattle from
2001-2005.\6\ Despite the EU BSE surveillance requirements for testing
all risk animals over 24 months of age and all healthy slaughter cattle
over 30 months of age, Figure 1 shows that application of the BSurvE
(Prevalence A) model to Netherlands BSE surveillance data does not
yield sufficient statistical power to draw clear distinctions among
birth year cohorts as prevalence declines (Figure 1).
---------------------------------------------------------------------------
\6\ The OIE Terrestrial Animal Code (Chapter 1.1.1., Article
1.1.1.1) defines incidence as ``the number of new cases or outbreaks
of a disease that occur in a population at risk in a particular
geographical area within a defined time interval (OIE 2006b).''
---------------------------------------------------------------------------
[[Page 53321]]
[GRAPHIC] [TIFF OMITTED] TR18SE07.023
Note that, in figure 1, there is a decrease in estimated prevalence
between 1998 birth-year cohorts and 1999 birth-year cohorts, while, at
the same time, there is an increase in the upper confidence limit. This
apparent paradox is indicative of another shortcoming of relying on
surveillance data alone to determine whether BSE prevalence has been
reduced. Because fewer animals from the most recent birth year cohorts
are tested when sent to slaughter, uncertainty about the prevalence in
the most recent cohorts is much greater than in older cohorts.
Furthermore, the lower likelihood of detecting BSE in young infected
animals means that the young animals that are tested contribute
relatively little to reducing uncertainty in the true (as opposed to
apparent) BSE prevalence. These two sources of uncertainty in young
birth cohorts (low numbers of animals tested, and little value in the
surveillance data that are gathered from them) cause an asymmetrical
increase in the upper limit of the confidence interval compared to the
lower confidence limit. This effect on the upper confidence limit on
BSE prevalence is most pronounced for the most recent birth year
cohorts which are less likely to be tested and will not have lived long
enough to manifest BSE, even if they have been infected. Wilesmith et
al. (2004, figure 3) further illustrates this same concept.
Consequently, if the effectiveness of a country's safeguards
against BSE amplification were determined strictly by setting a
tolerance for the upper confidence limit on BSE prevalence associated
with the ``real surveillance data,'' one might reach the incorrect
conclusion that prevalence is increasing, when in actuality, the result
is simply due to testing fewer and younger animals in the most recent
birth year cohorts. Finally, relying solely on surveillance data fails
to account for under reporting of disease due to the lack of diagnostic
sensitivity to detect BSE at an early stage of disease. By accounting
for the possibility of false negative test results, epidemiologic
models such as BSurvE are recognized as providing a more accurate
estimate of true BSE prevalence than the apparent prevalence measured
by surveillance data alone.
Issue: One commenter stated that the output from the BSurvE model
used by Canada in 2005 grossly underestimated Canada's 2006 and 2007
BSE prevalence and, therefore, the BSurvE model is unreliable for
estimating Canada's BSE prevalence. The commenter stated further that,
at the minimum, APHIS should determine the erroneous inputs that
resulted in the failed prediction in 2005 and correct them.
Response: In the risk assessment conducted for this rulemaking,
APHIS used its own prevalence estimate, not that of the Canadian Food
Inspection Agency's (CFIA's) 2006 prevalence estimate, which was not
based on BSurvE, but on a modified version that appears similar to the
APHIS BBC model. The commenter cites CFIA's Assessment of the North
American BSE Cases Diagnosed from 2003-2005 (Part II), which states
that ``when the BSurvE model was recently applied to Canada's
statistics and adjusted to account for the effectiveness of the 1997
feed ban (based on experiences with the 1988 feed ban in the United
Kingdom), the resulting prediction was that it could be expected that
three infected animals remain within the national herd'' (CFIA 2006, p.
13).
APHIS' estimation of BSE prevalence in Canada (APHIS 2006c) is that
the expected prevalence values under the BBC and BSurvE Prevalence B
models correspond to an expected number of BSE-infected animals in the
standing Canadian adult cattle population of 4.1 and 23.2,
respectively. APHIS further explains that it is important to note that
this range of prevalence estimates represents uncertainty and not
variability. BSE-infected animals are recruited into and exit from the
adult cattle population over time, but at a given point in time, the
number of infected animals in the population is a fixed but uncertain
value.
Assuming the overall probability of infection remains constant over
time, the actual number of infected cattle in the population at any
given point in time would still vary randomly about the mean. This
variability is incorporated in the model supporting the exposure
assessment for live bovines by means of the Poisson variability
distribution. Assuming a fixed mean prevalence of 4.1 and 23.2 BSE
infected animals in the standing adult cattle population in Canada, the
95th percentile of the Poisson distribution are 7 and 31 BSE-infected
animals in any given year, respectively. We note that these numbers are
greater than the
[[Page 53322]]
five BSE cases detected in Canada in 2006, which means that the
greatest number of Canadian BSE cases identified in a single
surveillance year is lower than even the 95th percentile of
distribution.
Issue: One commenter stated that, if the United States were finding
BSE cases at the same rate as in Canada, this would translate into
roughly 40 BSE cases detected in the United States since January 2006,
which would be regarded as a large number. The commenter stated further
that, at this time, the BSE situation in Canada does not appear to be
improving.
Response: We do not agree with the commenter. The commenter's
conclusion appears to be based on a cursory estimate and does not
provide an accurate comparison of BSE cases detected in Canada with a
comparable number that would have been detected in the United States,
given the larger U.S. cattle population. The commenter's comparison
fails to take into account other years of surveillance, as well as the
age and surveillance stream of tested animals. These data are extremely
important for estimating BSE prevalence. A comparison based solely on
the number of detected cases ignores infected animals with unapparent
or undetected infections.
Table 1 provides a direct comparison of the estimated BSE
prevalence in the current standing adult cattle population of the
United States and Canada, respectively, using identical estimation
methods (APHIS 2006a; 2006c).
Table 1.--Comparison of Estimated BSE Prevalence in the Current Standing
Adult Cattle Population of U.S. and Canada
------------------------------------------------------------------------
BSE Prevalence Estimation Method
----------------------------------------
Country BSurvE prevalence
B BBC
------------------------------------------------------------------------
Expected value
------------------------------------------------------------------------
US............................. 0.18 x 10-6........ 0.10 x 10-6
Canada......................... 3.9 x 10-6......... 0.68 x 10-6
------------------------------------------------------------------------
Despite the higher estimated BSE prevalence in the current standing
adult cattle population in Canada compared to the prevalence of BSE in
the standing adult cattle population in the United States, APHIS finds
that, because of the extremely low BSE prevalence in Canada and the
high levels of BSE controls in both Canada and the United States, the
risk to the United States (i.e., the likelihood of establishment of BSE
in the United States and the potential impacts of cases that may occur
even without establishment) as a result of importing from Canada the
bovine commodities considered in this rule is negligible (APHIS 2006b).
Furthermore, as stated in our risk assessment, we expect that the
prevalence of BSE in Canada will decrease continuously over the next
several years. Peer reviewers of our risk assessment agreed (RTI 2007).
Issue: One commenter stated that Canada's ratio of positive cases
per 10,000 cattle tested exceeds the ratio of 22 of the 25 EU-member
countries; that only the ratios for the United Kingdom, Portugal, and
Spain exceed Canada's 2006 ratio. The commenter noted further that even
the countries of Ireland, Germany, and France, each of which are
considered to have had widespread BSE exposure, have a lower ratio for
positive cases detected per 10,000 head tested than does Canada.
Another commenter stated that Canada's BSE prevalence is higher than
that for Denmark, Belgium, and Austria, and is comparable to the rate
in Germany. This commenter, who estimated the Canadian BSE prevalence
to be 6.4 cases per million cattle, stated further that no one
considers countries with a reported BSE rate of 1 to 2 cases per
million animals (e.g., Denmark, Belgium and Austria) to have a minimal
BSE risk, and that Canada is not a BSE minimal-risk region in any
ordinary sense.
Response: The commenters' statements ignore important differences
in BSE surveillance and cattle populations among countries, and a
comparison based simply on the proportion of positive cases per number
of cattle tested is inconsistent with the prevalence estimate approach
taken by one of the commenters, as well as the prevalence estimate used
by APHIS. Although calculating the proportion of infected animals
detected per number of tested animals can serve as a useful tool,
depending on the purpose for the calculation, it is not an estimate of
prevalence. Rather, prevalence is defined as the number of infected
animals in the total population at a given point in time. On the other
hand, the calculation conducted by the commenter who referred to the
ratio of positive cases per 10,000 cattle tested is similar to that
conducted by the U.S. Department of Health and Human Services, Centers
for Disease Control and Prevention (CDC). In May 2007, using data
similar to that analyzed by APHIS for this rulemaking, CDC calculated
the proportion of Canadian-born BSE cases identified by Canadian
authorities in relation to the total number of animals tested in that
country. CDC then made a like calculation regarding BSE cases in U.S.-
born cattle and compared the Canadian and U.S. results (CDC 2007).
Unlike the estimate used by APHIS in the risk assessment for this rule,
the CDC calculation is not an estimate of the prevalence of BSE in
Canada, nor of the prevalence in the United States. Although the type
of calculations conducted by CDC can be useful in comparing relative
proportions of BSE detections per number of cattle tested, they do not,
as noted above, constitute an estimate of prevalence.
The number of disease detections per total number of animals tested
can be influenced by the criteria used for choosing animals for
testing. For instance, Canada, like the United States, conducts
targeted BSE surveillance, sampling those animals where disease is most
likely to be detected if present. In contrast, EU countries routinely
test large numbers of healthy animals at slaughter. Approximately 80
percent of cattle tested for BSE in the EU during 2001-2004 were
healthy slaughtered animals, but ``risk animals'' were 22 times more
likely to test positive (EC 2005a). One study (Giovannini et al., 2005)
estimates the true prevalence of BSE infection in several EU countries.
Based on BSE test