-
ASSESSMENT
AND
CONTROL
OF
DNA
REACTIVE(MUTAGENIC)
IMPURITIES
IN
PHARMACEUTICALS TOLIMIT
POTENTIAL
CARCINOGENIC
RISK
为限制潜在致癌风险而对药
物中
DNA
活性(诱变性)杂质进行的评估和控制
M7
Current
Step 4
version
dated 23 June 2014
This
Guideline has been developed by the appropriate
ICH Expert Working Group and
has been
subject to consultation by the regulatory parties,
in accordance with the
ICH Process. At
Step 4 of the Process the final draft is
recommended for adoption
to the
regulatory bodies of the European Union, Japan and
USA.
M7
Document
History
文件历史
Code
文件代码
History
历史
M7
Date
日期
Approval by the Steering Committee
under Step 2
6 February 2013
and release for public consultation.
p>
第
2
阶段由筹委会批准,公开征求意见
p>
M7
Approval by the
Steering Committee under Step 4
5 June
2014
and
recommendation
for
adoption
to
the
three
ICH
regulatory bodies.
第
< br>4
阶段由筹委会批准,推荐
ICH
三方药监局采用
Current Step 4
version
现行版本第
4
阶段<
/p>
M7
Corrigendum
to
fix
typographical
errors
and
23 June 2014
replace word “degradants” with
“degradation
products” throughout the
document.
修
正
输
入
错
误
,
将
全
文
中
“
degradants
”
p>
替
换
成
“
degradation
products
”
.
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ASSESSMENT
AND
CONTROL
OF
DNA
REACTIVE
(MUTAGENIC)
IMPURITIES
IN
PHARMACEUTICALS TO
LIMIT
POTENTIALCARCINOGENIC
RISK
为限制潜在致癌风险而对药
物中
DNA
活性(诱变性)杂质进行的评估和控制
ICH Harmonised Tripartite
Guideline
ICH
三方协调指南
Having reached
Step 4
of the ICH Process at the ICH Steering
Committee meeting
on 5 June 2014, this
Guideline
is recommended for adoption
to the
three
regulatory
parties to ICH
TABLE OF
CONTENTS
1.
INTRODUCTION
2. SCOPE OF
GUIDELINE
3. GENERAL
PRINCIPLES
目录
概述
指南范围
通用原则
4.
CONSIDERATIONS FOR MARKETED PRODUCTS
上市产品应考虑的问题
4.1
Post-Approval
Changes
to
the
Drug
批准后原料药化学、生产和质量变更
Substance Chemistry, Manufacturing, and
Controls
4.2
Post-Approval
Changes
to
the
Drug
批准后制剂的化学、生产和质量变更
Product
Chemistry,
Manufacturing,
and
Controls
4.3
Changes
to
the
Clinical
Use
of
Marketed
上市产品临床使用变更
Products
4.4
Other
Considerations
for
Marketed
上市产品其它应考虑问题
Products
5.
DRUG
SUBSTANCE
AND
DRUG
PRODUCT
原料药和制剂杂质评估
IMPURITY ASSESSMENT
5.1 Synthetic Impurities
5.2 Degradation Products
5.3
Considerations
for
合成杂质
降解产物
Clinical
临床研发要考虑的问题
Development
6. HAZARD
ASSESSMENT ELEMENTS
7. RISK
CHARACTERIZATION
7.1 TTC-
based Acceptable Intakes
7.2
Acceptable
Intakes
Based
危害性评估要素
风险特征
根据
TTC
制订可接受摄入量
on <
/p>
根据化合物特定风险评估制订的可接受摄
入量
Compound-Specific Risk Assessments
7.2.1 Mutagenic Impurities with
Positive
致癌数据有利的诱变性杂质(表
1
中的第
1
Carcinogenicity
Data (Class 1 in Table 1)
类)
7.2.2
Mutagenic Impurities with Evidence
具有实用阈值证据的诱变性杂质
for a Practical Threshold
7.3 Acceptable Intakes
in
Relation to LTL
与
LTL
< br>暴露相关的可接受摄入量
Exposure
7.3.1 Clinical Development
7.3.2 Marketed Products
临床研发
已上市产品
7.4
Acceptable
Intakes
for
Multiple
多个诱变性杂质的可接受摄入量
Mutagenic Impurities
7.5
Exceptions
and
Flexibility
in
方法例外情况和弹性
Approaches
8.
CONTROL
控制
8.1
Control
of
Process
Related
Impurities
工艺相关杂质的控制
8.2
Considerations
for
Control
Approaches
控制方法要考虑的问题
8.3 Considerations for Periodic
Testing
定期检查要考虑的问题
8.4
Control of Degradation Products
8.5 Lifecycle Management
8.6
Considerations
for
降解产物的控制
生命周期管理
Clinical
临床研发要考虑的问题
Development
9.
DOCUMENTATION
9.1 Clinical
Trial Applications
文件记录
临床试验应用
9.2 Common
Technical Document (Marketing
通用技术文件(上市申报)
Application)
NOTES
GLOSSARY
REFERENCES
APPENDICES
注解
术语
参考文献
附录
ASSESSMENT
AND
CONTROL
OF
DNA
REACTIVE
(MUTAGENIC)
IMPURITIES
IN
PHARMACEUTICALS TO
LIMIT
POTENTIALCARCINOGENIC
RISK
为限制潜在致癌风险而对药
物中
DNA
活性(诱变性)杂质进行的评估和控制
1. INTRODUCTION
概述
The
synthesis
of
drug
substances
involves
the
use
of
reactive
chemicals,
reagents,
solvents,
catalysts, and other processing aids. As a result
of chemical synthesis
or
subsequent
degradation,
impurities
reside
in
all
drug
substances
and
associated
drug products.
While ICH Q3A(R2): Impurities in New Drug
Substances and Q3B(R2):
Impurities
in
New
Drug
Products
(Ref.
1,
2)
provides
guidance
for
qualification
and
control
for
the
majority
of
the
impurities,
limited
guidance
is
provided
for
those
impurities that are
DNA reactive. The purpose of this guideline is to
provide a
practical
framework
that
is
applicable
to
the
identification,
categorization,
qualification,
and
control
of
these
mutagenic
impurities
to
limit
potential
carcinogenic risk.
This guideline is intended to complement ICH
Q3A(R2), Q3B(R2)
(Note 1), and ICH
M3(R2): Nonclinical Safety Studies for the Conduct
of Human
Clinical Trials and Marketing
Authorizations for Pharmaceuticals (Ref. 3).
原料药合成牵涉到使用活性化学物质、试剂、
溶剂、
催化剂和其它工艺助剂,
导致在所有原
料药及其制剂中会残留
有化学合成或其降解产物、杂质。在
ICH
Q3A(R2)<
/p>
新原料药中的杂质
和
Q3B(R2)
p>
新制剂中的杂质(参考文献
1
、
2
)中提供了关于主要杂质定性和控制的指南,对
DNA
活性杂质给出了有限的指南。本指南的目的是提供实用框架,以应用于这些诱变杂
质的
鉴别、
分类、
定性和控制,
对潜在致癌风险进行控制。
本指南意在补充
I
CH
Q3A(R2)
、
Q3B(R2
)
(注解
1
)
和
ICH
M3(R2)
药物人用临床
试验和上市许可中的非临床安全性研究
(参考文献
3
)
。
This
guideline
emphasizes
considerations
of
both
safety
and
quality
risk
management
in
establishing
levels
of
mutagenic
impurities
that
are
expected
to
pose
negligible
carcinogenic
risk.
It
outlines
recommendations
for
assessment
and
control
of
mutagenic
impurities
that
reside
or
are
reasonably
expected
to
reside
in
final
drug
substance or product,
taking into consideration the intended conditions
of human
use.
本指
南强调在建立诱变性杂质水平时考虑安全性和质量风险管理两方面,
该水平应该仅表现<
/p>
出可忽略不计的致癌风险。
指南在考虑药物在人用时的条件下,<
/p>
给出了对原料药或制剂中残
留或可能残留的诱变性杂质评估和控制
的建议。
2. SCOPE OF
GUIDELINE
指南适用范围
This document is
intended to
provide
guidance
for new
drug substances
and new drug
products
during
their
clinical
development
and
subsequent
applications
for
marketing. It also
applies to post-approval submissions of marketed
products, and
to new marketing
applications for products with a drug substance
that is present
in a previously
approved product, in both cases only where:
本指南意在给研发期间和上市申报期间的新原料药和新制剂提供指南。
它也适
用于已上市药
物的批准后申报,以及之前已批准上市的制剂中的同样原料药生产的另一制
剂新上市申报。
当上述申报符合以下情形时:
—
Changes to the drug substance synthesis
result in new impurities
or increased
acceptance criteria for existing impurities;
—
原料药合成变更,导致产生新杂质或已有杂质可接受标准增加
—
Changes in the formulation, composition
or manufacturing process
result
in
new
degradation
products
or
increased
acceptance
criteria
for
existing
degradation products;
—
p>
配方变更、
组分变更或生产工艺变更,
导致
产生新的降解产物或已有降解
产物可接受标准增加
—
Changes
in
indication
or
dosing
regimen
are
made
which
significantly affect the acceptable
cancer risk level.
—
指征变更或给药方案变更,导致可
接受癌症风险水平受到重大影响
Assessment
of
the
mutagenic
potential
of
impurities
as
described
in
this
guideline
is not intended
for the following types of drug substances and
drug products:
biological/biotechnological,
peptide,
oligonucleotide,
radiopharmaceutical,
fermentation products, herbal products,
and crude products of animal or plant
origin.
本指南中描述的杂质潜在诱变性评估不适用于
以下类型的原料药和制剂:生物
/
生物技术制
< br>品、肽类、寡核苷酸、放射药物、发酵产品、草药制品和动物或植物来源的粗品。
This guideline does not apply to drug
substances and drug products intended for
advanced
cancer
indications
as
defined
in
the
scope
of
ICH
S9
(Ref.
4).
Additionally,
there may be
some cases where a drug substance intended for
other indications is
itself
genotoxic
at
therapeutic
concentrations
and
may
be
expected
to
be
associated
with
an
increased
cancer
risk.
Exposure
to
a
mutagenic
impurity
in
these
cases
would
not
significantly
add
to
the
cancer
risk
of
the
drug
substance.
Therefore,
impurities could
be controlled at acceptable levels for non-
mutagenic impurities.
本指南不适用于
ICH
S9
(参考文献
4
)中所定义的晚期癌症指征用原料
药和制剂。另外,可
能会有些情况下,
制剂用于其它治疗,
p>
而其自己本身在治疗浓度下就具有基因毒性,
已知其
会使癌症风险增加。
这些情况下,
暴露在具有诱变性的
杂质下,
不会显著增加原料药的癌症
风险。因此,杂质可以被控
制在非诱变性杂质的可接受水平。
Assessment
of
the
mutagenic
potential
of
impurities
as
described
in
this
guideline
is
not
intended
for
excipients
used
in
existing
marketed
products,
flavoring
agents
,
colorants,
and
perfumes.
Application
of
this
guideline
to
leachables
associated
with
drug product packaging is not intended,
but the safety risk assessment principles
outlined
in
this
guideline
for
limiting
potential
carcinogenic
risk
can
be
used
if
warranted. The safety
risk assessment principles of this guideline can
be used if
warranted for impurities in
excipients that are used for the first time in a
drug
product and are chemically
synthesized.
在本指南中所描述的对杂质潜在诱
变性的评估不适用于已上市药物中使用的辅料、调味剂、
着色剂和香料。
本指南不适用于药物包材中的可浸出杂质,
但指南中限制潜在致癌风险的安
p>
全风险评估原则在一定情况下是可以使用的。
如果辅料是首次用于药
物中,
且是化学合成的,
则本指南的安全风险评估原则可以适用
于辅料中的杂质。
3. GENERAL
PRINCIPLES
通用原则
The focus of this guideline is on DNA
reactive substances that have a potential to
directly cause DNA damage when present
at low levels leading to mutations and
therefore,
potentially
causing
cancer.
This
type
of
mutagenic
carcinogen
is
usually
detected in a bacterial reverse
mutation (mutagenicity) assay. Other types of
genotoxicants
that
are
non-mutagenic
typically
have
threshold
mechanisms
and
usually do not pose
carcinogenic risk in
humans
at the level
ordinarily
present as
impurities.
Therefore to limit a possible human cancer risk
associated with the
exposure to
potentially mutagenic impurities, the bacterial
mutagenicity assay is
used to assess
the mutagenic potential and the need for controls.
Structure-based
assessments are useful
for predicting bacterial mutagenicity outcomes
based upon
the
established
knowledge.
There
are
a
variety
of
approaches
to
conduct
this
evaluation including a review of the
available literature, and/or computational
toxicology assessment.
本指南关注的焦点为可与
DNA
反应的物质,这些
物质在较低水平时也可能会直接引起
DNA
损伤,导致
DNA
诱变,从而引发癌症。这类诱变性致癌作用常被细菌逆式突变(诱
变)含量
检出。
其它类型不具有典型诱变性的基因毒性物质则有
阈值进行控制,
一般以常规水平杂质
出现时对人类不具有致癌风
险。
因此,
为了限制暴露于潜在诱变性杂质可能带来的人类癌症
风险,
我们使用细菌诱变含量来评估诱变可能性及控制的必要性
。
基于结构进行的评估有助
于根据已有的知识来预测细菌诱变性
测试结果。
有很多方法可以用于实施该评估,
包括对可
获得的文献资料进行审核,和
/
或采用计算方式
进行毒性评估。
A Threshold of
Toxicological Concern (TTC) concept was developed
to define an
acceptable
intake
for
any
unstudied
chemical
that
poses
a
negligible
risk
of
carcinogenicity
or
other
toxic
effects.
The
methods
upon
which
the
TTC
is
based
are
generally considered to be very
conservative since they involve a simple linear
extrapolation
from
the
dose
giving
a
50%
tumor
incidence
(TD50)
to
a
1
in
106incidence,
using TD50
data for the most
sensitive species and most sensitive site of tumor
induction. For application of a TTC in
the assessment of acceptable limits of
mutagenic impurities in drug substances
and drug products, a value of 1.5
μ
g/day
corresponding
to
a
theoretical
10-5
excess
lifetime
risk
of
cancer,
can
be
justified. Some structural
groups were identified to be of such high potency
that
intakes even below the TTC would
theoretically be associated with a potential for
a significant carcinogenic risk. This
group of high potency mutagenic carcinogens
referred to as the “cohort of concern”,
co
mprises aflatoxin-like-, N-nitroso-,
and alkyl-azoxy compounds.
<
/p>
已经建立了
TTC
概念,
用于界定所有未经研究,
但具有可忽略的致癌风险或其它毒性效果的
化学品的可接受摄入量。
基于
TTC
的方法一般被认为是非常保守的,
因为它们牵涉到从给定
的
50%
肿瘤发生率(
TD50<
/p>
)简单线性外推到十万分之一发生率,且采用的数据是来自于最敏
感物种和最敏感肿瘤部位的
TD50
数据。在使用
TTC
评估原料药和制剂中诱变性杂质的可接
爱标准
时,可以采用
1.5
μ
g/
天对应于十万分之一生命时长患癌风险。有些结构基团被识别
为具有较高的
效价,
因此即使摄入量低于
TTC
水平
,
从理论上来说仍会导致可能的显著癌症
风险。这类具有较高效
价的基团被称为“关注队列”,包括黄曲霉素类、
N-
亚硝基化
合物,
以及烷基
-
氧化偶氮基化合物。
During
clinical
development,
it
is
expected
that
control
strategies
and
approaches
will be less developed in earlier
phases where overall development experience is
limited.
This
guideline
bases
acceptable
intakes
for
mutagenic
impurities
on
established
risk
assessment
strategies.
Acceptable
risk
during
the
early
development phase is set at a
theoretically calculated level of approximately
one
additional cancer per million. For
later stages in development and for marketed
products, acceptable increased cancer
risk is set at a theoretically calculated
level of approximately one in one
hundred thousand. These risk levels represent a
small
theoretical
increase
in
risk
when
compared
to
human
overall
lifetime
incidence
of developing any type of cancer, which
is greater than 1 in 3.
在临床研
发期间,
如果整体研发经验有限,
在早期临床阶段对控制策略和
控制方法的要求会
较低。
本指南是在已建立的风险评估策略的基
础上,
制订诱变性杂质的可接受摄入量。
在早
< br>期研发阶段,
可接受风险是建立在患癌率约为百万分之一的理论计算水平上的。<
/p>
在研发后期
及上市后,
可接受癌症增加风
险是建立在患癌率约为十万分之一的理论计算水平上的。
相较
于人类整个生命周期罹患各类癌症的发生率
(大于三分之一)<
/p>
,
这两个不同的风险水平在理
论上风险稍
有增加。
It
is
noted
that
established
cancer
risk
assessments
are
based
on
lifetime
exposures.
Less-Than-Lifetime (LTL) exposures both
during development and marketing can have
higher
acceptable
intakes
of
impurities
and
still
maintain
comparable
risk
levels.
已注意到所建立的患
癌风险评估是根据生命周期内暴露情形的。
在研发期间和上市期间低于
< br>生命周期(
LTL
)暴露都可能允许摄入更多杂质,仍保
留一定的风险水平。
The use of a
numerical cancer risk value (1 in 100,000) and its
translation into
risk-based
doses
(TTC)
is
a
highly
hypothetical
concept
that
should
not
be
regarded
as a
realistic indication of the actual
risk.
使用量化患癌风险值(十万分之一),并将其转化
为根据风险计算的剂量(
TTC
值)是一种
高度假想的概念,不应作为真实风险的一种实际指标。
Nevertheless,
the
TTC
concept
provides
an
estimate
of
safe
exposures
for
any
mutagenic compound.
< br>不管怎样,
TTC
概念提供了对诱变性化合物下安全暴露
的一种估计方法。
However, exceeding
the TTC is not necessarily associated with an
increased cancer
risk
given
the
conservative
assumptions
employed
in
the
derivation
of
the
TTC
value.
但是,假出在
TTC
值计算时采用了保守假设,超出
TTC<
/p>
值并不一定会伴随患癌风险增加。
The
most
likely
increase
in
cancer
incidence
is
actually
much
less
than
1
in
100,000.
In
addition, in cases where a mutagenic compound is a
non-carcinogen in a rodent
bioassay,
there
would
be
no
predicted
increase
in
cancer
risk.
Based
on
all
the
above
considerations, any exposure to an
impurity that is later identified as a mutagen
is not necessarily associated with an
increased cancer risk for patients already
exposed to the impurity. A risk
assessment would determine whether any further
actions would be taken.
大多数患癌可能性实际远低于十万分之一,
另外,
如果有一个诱变性化合物在啮齿动物生物
含量中显示为非诱变性,
则预测其致癌风险不会增加。
基于上述这些原因,
所有暴露
在之后
鉴定为诱变性杂质并不一定伴随已暴露于该杂质的患者
癌症风险增加。
应进行风险评估来决
定是否需要采取进一步行动
。
Where
a
potential
risk
has
been
identified
for
an
impurity,
an
appropriate
control
strategy leveraging process
understanding and/or analytical controls should be
developed
to
ensure
that
the
mutagenic
impurity
is
at
or
below
the
acceptable
cancer
risk level.
如果一个杂
质被鉴定为具有潜在风险,则需要采用一个适当的控制策略来平衡工艺知识和
/
或分析控制,以保证诱变性杂质等于或低于可接受的癌症风险水平。
There may be cases when an impurity is
also a metabolite of the drug substance. In
such cases the risk assessment that
addresses mutagenicity of the metabolite can
qualify the impurity.
有时一种杂质可能也是药品的一种代谢产物,
这时,
对代谢产物的诱变性风险评估可以用于
支持该杂质的质量水平。
4. CONSIDERATIONS
FOR
MARKETED
PRODUCTS
已上市药品要考虑的问题
This
guideline is not intended to be applied
retrospectively (i.e., to products
marketed
prior
to
adoption
of
this
guideline).
However,
some
types
of
post-approval
changes
warrant a reassessment of safety relative to
mutagenic impurities. This
section
applies to these post-approval changes for
products marketed prior to, or
after,
the
adoption
of
this
guideline.
Section
8.5
(Lifecycle
Management)
contains
additional
recommendations
for
products
marketed
after
adoption
of
this
guideline.
<
/p>
本指南无意回顾性地应用于在指南采纳前已上市的药物。
但是,<
/p>
有些类型的批准后变更需要
对有关的诱变性杂质安全性重新进行评
估。
本部分适用于在指南被采纳前后上市药品的该类
批准后的变
更。第
8.5
(生命周期管理)包括了对采纳本指南后已上市药
品的其它建议。
4.1 Post-Approval
Changes to the Drug Substance Chemistry,
Manufacturing, and
Controls
上市后变更
---
原料药研发、生产和控制
Post-approval submissions involving
the drug substance chemistry, manufacturing,
and controls should include an
evaluation of the potential risk impact associated
with
mutagenic
impurities
from
changes
to
the
route
of
synthesis,
reagents,
solvents,
or
process
conditions
after
the
starting
material.
Specifically,
changes
should
be
evaluated to determine if the changes
result in any new mutagenic impurities or
higher
acceptance
criteria
for
existing
mutagenic
impurities.
Reevaluation
of
impurities not impacted
by changes is not recommended. For example, when
only a
portion
of
the
manufacturing
process
is
changed,
the
assessment
of
risk
from
mutagenic impurities should be limited
to whether any new mutagenic impurities
result
from
the
change,
whether
any
mutagenic
impurities
formed
during
the
affected
step
are
increased,
and
whether
any
known
mutagenic
impurities
from
up-stream
steps
are
increased.
Regulatory
submissions
associated
with
such
changes
should
describe
the
assessment
as
outlined
in
Section
9.2.
Changing
the
site
of
manufacture
of
drug
substance,
intermediates,
or
starting
materials
or
changing
raw
materials
supplier
will not require a reassessment of
mutagenic impurity risk.
批准后
申报涉及原料药的研发、
生产和控制应包括起始物料后的合成路线、
试剂、
溶剂或工
艺条件变更时,
诱
变性杂质对潜在风险影响的评估。
特别是,
变更评估要确定其是
否会导致
任何新的诱变性杂质或已知诱变性杂质会有更高的可接受标准。
不建议对不受变更影响的杂
质重新进行评估。
例如,<
/p>
如果只有一部分生产工艺发生变更,
则诱变性杂质的风险评估应局
限于该变更是否会产生新的诱变性杂质、
在受影响的步骤中是否
有诱变性杂质含升高,
以及
上游步骤中的已知诱变性杂质是否升
高。
该变更发生时提交的法规申报资料应描述
9.2
中所
列的评估。
对原料药、
中间体或起始物料的生产场所的变更,
或变更原料供应商则不需要对
< br>诱变性杂质风险重新进行评估。
When a new
drug substance supplier is proposed, evidence that
the drug substance
produced by this
supplier using the same route of synthesis as an
existing drug
product
marketed
in
the
assessor’s
region
is
considered
to
be
sufficient
evidence
of
acceptable
risk/benefit
regarding
mutagenic
impurities
and
an
assessment
per
this
guideline is not
required. If this is not the case, then an
assessment per this
guideline is
expected.
如果拟提交一
个新的原料药供应商,
如有证据证明该供应商生产的原料药采用了与审评区域
内已上市制剂中所用的原料药具有相同的合成路线,则足以说明关于诱变性杂质其风险
/
利
益是可以接受的,
不需
要根据本指南进行评估。
如果不同这样,
则需要根据本指南进行
评估。
4.2
Post-
Approval
Changes
to
the
Drug
Product
Chemistry,
Manufacturing,
and
Controls
上市后变
更
---
制剂研发、生产和控制
Post-approval
submissions
involving
the
drug
product
(e.g.,
change
in
composition,
manufacturing
process, dosage form) should include an evaluation
of the potential
risk associated with
any new mutagenic degradation products or higher
acceptance
criteria
for
existing
mutagenic
degradation
products.
If
appropriate,
the
regulatory submission
would include an updated control strategy.
Reevaluation of
the drug substance
associated with drug products is not recommended
or expected
provided
there
are
no
changes
to
the
drug
substance.
Changing
the
site
of
manufacture
of drug product
will not require a reassessment of mutagenic
impurity risk.
上市后申报如果涉及制剂(例
如、成分、生产工艺、剂型),则应包括对所有新的诱变性降
解产物或已有诱变性降解产
物更高的可接受标准进行评估。
适当时,
法规申报资料应包括对
控制策略的更新。
如果原料药并没有发生变更,
则不建议,
也不期望对制剂相关的原料药重
新进行评估
,制剂生产场所变更不需要对诱变性杂质风险重新进行评估。
4.3 Changes to the Clinical Use of
Marketed Products
上市后药品临床使用变更
Changes to the clinical use of marketed
products that can warrant a reevaluation
of the mutagenic impurity limits
include a significant increase in clinical dose,
an
increase
in
duration
of
use
(in
particular
when
a
mutagenic
impurity
was
controlled
above
the
lifetime
acceptable
intake
for
a
previous
indication
that
may
no
longer
be
appropriate
for
the
longer
treatment
duration
associated
with
the
new
indication), or for a change in
indication from a serious or life threatening
condition
where
higher
acceptable
intakes
were
justified
(Section
7.5)
to
an
indication for a less serious condition
where the existing impurity acceptable
intakes may no longer be appropriate.
Changes to the clinical use of marketed
products associated with new routes of
administration or expansion into patient
populations
that
include
pregnant
women
and/or
pediatrics
will
not
warrant
a
reevaluation, assuming no increases in
daily dose or duration of treatment.
p>
已上市药品的临床应用变更拒收情节包括,
变更所引起的对诱变杂质
限度的重新评估中会包
括临床使用剂量的显著增加、
用药时长的
增加
(特别是当根据之前的指征,
将诱变性杂质控
制在超出生命全程使用时可接受摄入量时,
可能采用新的指征,
其原定摄入量已不再适用于
更长的治疗时长。
)
p>
或者是指征变更是从已论述的在病情较严重或危及生命的病患状态下采
用较高可接受摄入量的情况,
变成不那么严重的病患情况,
原
有的杂质可接受摄入量可能不
再适当了。如果已上市药品的临床应用变更包涵有使用新的
给药途径,或扩大使用患者群,
从而包括孕妇和
/
或小儿,假定日剂量或用药时长不增加,则无法保证重新评估符合要求。
4.4 Other Considerations for Marketed
Products
已上市药物的其它需考虑问题
Application of this guideline may be
warranted to marketed products if there is
specific cause for concern. The
existence of impurity structural alerts alone is
considered
insufficient
to
trigger
follow-up
measures,
unless
it
is
a
structure
in
the cohort of concern (Section 3).
However a specific cause for concern would be
new
relevant
impurity
hazard
data
(classified
as
Class
1
or
2,
Section
6)
generated
after
the
overall
control
strategy
and
specifications
for
market
authorization
were
established.
This
new
relevant
impurity
hazard
data
should
be
derived
from
high-quality
scientific
studies
consistent
with
relevant
regulatory
testing
guidelines, with data records or
reports readily available. Similarly, a newly
discovered impurity that is a known
Class 1 or Class 2 mutagen that is present in
a marketed product could also be a
cause for concern. In both of these cases when
the
applicant
becomes
aware
of
this
new
information,
an
evaluation
per
this
guideline
should be conducted.
本指南在某些特殊原因考虑时可以适用于已上市的药品。
仅凭杂质存在警示结构
是无法启动
后续措施的,除非该结构具有队列方面的担忧
(第<
/p>
3
部分)。所谓的一种特殊顾虑原因可以
是在上市产品已建立其总体控制策略和质量标准后所获得的新的相关杂质危害数据
(分类
为
第
1
或和
2
类,
第
6
部分
)
。
这些新的相关杂质危害性数据所采用的研究方法应具有高质
量
科学性,且与相关的法规测试指南相一致,其数据记录或报告应易于获得。
类似地,在已上
市药品中发现一个新的杂质,<
/p>
且被确知属于第
1
类或第
2
类诱变性,
则也属于一种特殊顾虑
< br>原因。上述两种情形下,一旦申报人知晓这些新的信息,则需要实施本指南所要求的评估。
5. DRUG
SUBSTANCE AND
DRUG
PRODUCT
IMPURITY
ASSESSMENT
原料药和制剂杂质评
估
Actual and potential impurities that
are likely to arise during the synthesis and
storage
of
a
new
drug
substance,
and
during
manufacturing
and
storage
of
a
new
drug
product should be assessed.
实际存在和可能存在的杂质是可能在新原料药合成和存贮过程、
生产过程中生成。
对新制剂
的存贮条件应进行评估。
The impurity assessment is a
two-stage process:
杂质评估可以分为两个阶段:
—
Actual impurities that have been
identified should be considered
for
their mutagenic potential.
—
已被鉴定的实际存在的杂质应考虑其潜在诱变性
—
An assessment of potential impurities
likely to be present in the
final
drug
substance
is
carried
out
to
determine
if
further
evaluation
of
their
mutagenic potential is
required.
—
对可能存在于原料药中的潜在杂质
进行评估,
以确定是否需要对其潜在诱
变性进行进一步评估
p>
The
steps
as
applied
to
synthetic
impurities
and
degradation
products
are
described
in Sections 5.1
and 5.2, respectively.
适用于合成
杂质和降解产物的方法分别在第
5.1
和
5.2
部分进行了描述。
5.1
Synthetic Impurities
合成杂质
Actual
impurities include those observed in the drug
substance above the ICH Q3A
reporting
thresholds. Identification of actual impurities is
expected when the
levels
exceed
the
identification
thresholds
outlined
by
ICH
Q3A.
It
is
acknowledged
that
some
impurities
below
the
identification
threshold
may
also
have
been
identified.
实际杂质包括原料药中超出
ICH
Q
3A
报告阈的杂质。如果杂质水平超过了
ICH
Q3A
中所述的
鉴别阈,则需要进行鉴别。有些低于
鉴别阈的杂质可能也是经过鉴别的。
Potential
impurities
in
the
drug
substance
can
include
starting
materials,
reagents
and intermediates
in
the route of synthesis from the
starting material to the drug
substance.
原料药中潜在
杂质可以包括起始物料、试剂和从起始物料到原料药合成路线中的中间体,
The risk of carryover into the drug
substance should be assessed for identified
impurities
that
are
present
in
starting
materials
and
intermediates,
and
impurities
that
are
reasonably
expected
by-products
in
the
route
of
synthesis
from
the
starting
material
to
the
drug
substance.
As
the
risk
of
carryover
may
be
negligible
for
some
impurities (e.g., those
impurities in early synthetic steps of long routes
of
synthesis), a risk-based
justification could be provided for the point in
the
synthesis after which these types
of impurities should be evaluated for mutagenic
potential.
应评估起始物
料和中间体中的杂质,
以及从起始物料到原料药的合成路线中会生成的副产物
被带入原料药的风险。
由于有些杂质被带入原料药的风险可以忽略
(例如,
很长的合成路线
中较早的合成步骤中的
杂质),可以提交对这些杂质在合成路线某一点时基于风险的论述。
在合成路线该点之后
,此类杂质需要评估其诱变可能性。
For
starting
materials
that
are
introduced
late
in
the
synthesis
of
the
drug
substance
(and
where
the
synthetic
route
of
the
starting
material
is
known)
the
final
steps
of
the
starting
material
synthesis
should
be
evaluated
for
potential
mutagenic
impurities.
对于在原料
药合成路线后期才引入的起始物料
(以及如果已知起始物料的合成路线)
,
需要
评估起始物料合成的最终步骤中的潜在诱变性杂
质。
Actual
impurities
where
the
structures
are
known
and
potential
impurities
as
defined
above
should be evaluated for mutagenic potential as
described in Section 6.
已知其结
构的实际杂质和如上所述的潜在杂质应按第
6
部分要求评估其潜
在诱变性。
5.2 Degradation
Products
降解产物
Actual
drug
substance
degradation
products
include
those
observed
above
the
ICH
Q3A
reporting
threshold
during
storage
of
the
drug
substance
in
the
proposed
long-term
storage
conditions
and
primary
and
secondary
packaging.
Actual
degradation
products
in the drug product
include those observed above the ICH Q3B reporting
threshold
during
storage
of
the
drug
product
in
the
proposed
long-term
storage
conditions
and
primary
and
secondary
packaging,
and
also
include
those
impurities
that
arise
during
the
manufacture
of
the
drug
product.
Identification
of
actual
degradation
products
is expected when the levels exceed the
identification thresholds outlined by ICH
Q3A/Q3B.
It
is
acknowledged
that
some
degradation
products
below
the
identification
threshold may also have been
identified.
原料药实际降解产物包括原料药在内
包装和外包装内,
在拟定的长期存贮条件下原料药存贮
期间观察
到的高于
ICH
Q3A
报告阈值的物
质。
制剂中实际降解产物包括制剂在内包装和外包
装内,在拟定
的长期存贮条件下原料药存贮期间观察到的高于
ICH
Q3B
报告阈值的物质,还
包括在制剂生产过程中产生的那些杂质。<
/p>
如果降解产物的含量水平超过
ICH
Q
3A/Q3B
的鉴别
阈,则应进行鉴别。有些低于鉴别阈值的降
解产物可能也是经过鉴别的。
Potential
degradation
products
in
the
drug
substance
and
drug
product
are
those
that
may be
reasonably expected to form during long term
storage conditions. Potential
degradation products include those that
form above the ICH Q3A/B identification
threshold during accelerated stability
studies
(e.g., 40°C/75% relative
humidity
for
6
months)
and
confirmatory
photo-stability
studies
as
described
in
ICH
Q1B
(Ref.
5),
but
are
yet
to
be
confirmed
in
the
drug
substance
or
drug
product
under
long-term
storage conditions
in the primary packaging.
原料
药和制剂中潜在的降解产物是指经过合理推测,在长期存贮条件下可能会形成的物质。
潜
在降解产物包括在加速稳定性试验中(例如
40°C/75%下
6
个月)和
ICH
Q1B(
参考文
献
5)
光照稳定性试验中形成的超出
ICH Q3A/B
的鉴别限,但在原料药和制剂内包装长期存
贮条件下尚未确认的物质。
Knowledge
of relevant degradation pathways can be used to
help guide decisions on
the selection
of potential degradation products to be evaluated
for mutagenicity
e.g., from degradation
chemistry principles, relevant stress testing
studies, and
development stability
studies.
相关降解途径的知识有助于指导选择性地评
估潜在降解产物的诱变性,
例如,
从降解化学原
理、相关强降解试验和研发稳定性研究。
Actual and potential degradation
products likely to be present in the final drug
substance or drug product and where the
structure is known should
be evaluated
for
mutagenic potential as
described in Section 6.
实际存在
和可能存在于最终原料药或制剂中的降解产物只要知道结构,
均应根据第
6
部分要
求评估其诱变可能性。
5.3 Considerations for Clinical
Development
临床研发中要考虑的问题
It
is
expected
that
the
impurity
assessment
described
in
Sections
5.1
and
5.2
applies
to
products
in
clinical
development.
However,
it
is
acknowledged
that
the
available
information is limited. For example,
information from long term stability studies
and photo-stability studies may not be
available during clinical development and
thus information on potential
degradation products may be limited. Additionally,
the
thresholds
outlined
in
ICH
Q3A/B
do
not
apply
to
products
in
clinical
development
and consequently
fewer impurities will be identified.
p>
要求在临床阶段应用第
5.1
和
5.2
部分对杂质进行评估。
但是,
众所周知可能获得的信息会
比较有限。
例如,
在临床阶段可能还没有长期稳定性研究和光照稳定性试验数据,
因此关
于
潜在降解杂质的资料可能比较有限。另外,在
ICH
Q3A/B
中列出的阈值不适用于临床阶段的
药品,因此被鉴别出的杂质会很少。
6. HAZARD
ASSESSMENT
ELEMENTS
危害性评估要素
Hazard assessment involves an initial
analysis of actual and potential impurities
by conducting database and literature
searches for carcinogenicity and bacterial
mutagenicity data in order to classify
them as Class 1, 2, or 5 according to Table
1.
If
data
for
such
a
classification
are
not
available,
an
assessment
of
Structure-Activity
Relationships
(SAR)
that
focuses
on
bacterial
mutagenicity
predictions
should
be
performed.
This
could
lead
to
a
classification
into
Class
3,
4, or
5.
危害性分析会涉及采用数据库和诱变和细菌诱变数据文献
检索启动对实际和可能杂质的分
析,以根据表
1
将其分类为第
1
类、
第
2
类或第
5
类。如果
无法获得这样的分类数据,
则应
进行结构
-
活性关系(
SAR
)评估,该评估
应着重关注细菌诱变性预期。
这时可能会使得该杂
质被分入第<
/p>
3
类、第
4
类或
第
5
类。
Table 1: Impurities Classification with
Respect to Mutagenic and Carcinogenic
Potential and Resulting Control
Actions
Class
Definition
Proposed action
for control (details in
Section 7 and
8)
1
Known mutagenic
carcinogens
Control at or below
compound-specific
acceptable limit
2
Known
mutagens
with
unknown
Control at or below acceptable limits
carcinogenic
(bacterial
positive*,
potential
(appropriate TTC)
mutagenicity
no
rodent
carcinogenicity data)
3
Alerting structure,
unrelated
Control at or below
acceptable limits
to the structure of
the drug
(appropriate TTC) or conduct
bacterial
substance:
no
mutagenicity
mutagenicity
assay:
data
If non-mutagenic
= Class 5
If mutagenic = Class 2
4
Alerting
structure,
same
alert
Treat as non-mutagenic
impurity
in
drug
substance
or
compounds
related to the
drug substance
(e.g., process
intermediates)
which
have
been
tested
and
are
non-mutagenic
5
No
structural
alerts,
or
Treat
as non-mutagenic impurity
alerting
structure
with
sufficient
data
to
demonstrate
lack
of
mutagenicity
or
carcinogenicity
*Or
other
relevant
positive
mutagenicity
data
indicative
of
DNA-reactivity
related
induction of gene
mutations (e.g., positive findings in
in vivo
gene mutation
studies)
表
1
:根据诱变性和致癌性及其控制措施对杂质分类
分类
1
2
定义
已知诱变致癌性
已知具有诱变性,致
癌效应未知
(细菌诱变呈阳性
*
,
p>
无啮齿动物
致癌数据)
3
警示结构,与原料药结构无关,<
/p>
无诱变性数据
控制不高于可接受限度(
适当的
TTC
)或检
测细菌诱变含量:
如果非诱变性
=
第
5
类
如果具有诱变性
=
第
2
类
4
警示结构,与原料药或有关物质<
/p>
有相同警示
(例如,
工艺中间体)
,
经测试为无诱变性
5
无警示结构,或警示结果具有充<
/p>
与非诱变性杂质同等对待
与非诱变性杂质同等对待
拟定控制措
施(详见第
7
和
8
部分)
控制不高于化合物可接受限度
控制不
高于可接受限度(适当的
TTC
)
分的数据证明其不具备诱变性和
致癌性
*
或其它相关阳性诱变数据,说明与诱导基因变性的
DNA
反应活性(例如,体内基因诱变研
究显示阳
性)
A
computational
toxicology
assessment
should
be
performed
using
(Q)SAR
methodologies
that
predict
the
outcome
of
a
bacterial
mutagenicity
assay
(Ref.
6).
Two (Q)SAR prediction methodologies
that complement each other should be applied.
One methodology should be expert rule-
based and the second methodology should be
statistical-based. (Q)SAR models
utilizing these prediction methodologies should
follow
the
general
validation
principles
set
forth
by
the
Organisation
for
Economic
Co-operation and
Development (OECD).
应采用(
Q
)
SAR
方法进行计
算学毒性评估,预测细菌诱变含量(参考文献
6
)的结果。要使
用两个相互补充的(
Q
)
SAR
预测方法。一个方法应是依据专家规则的,另一个方法则应该
是统计方式的。
(Q)SAR
模式采用的这些预
测方法应服从
OECD
制订的通用验证原则。
< br>
The
absence
of
structural
alerts
from
two
complementary
(Q)SAR
methodologies
(expert
rule-based and statistical) is
sufficient to conclude that the impurity is of no
mutagenic concern, and no further
testing is recommended (Class 5 in Table
1).
两个互补的(
Q
)
SAR
方法(专家规则和统计学)如果没有发现结
构警示,则足以得出结论
该杂质没有诱变可能,不需要做进一步的检测(表
1
中第
5
类)。
If
warranted,
the
outcome
of
any
computer
system-based
analysis
can
be
reviewed
with
the use of expert
knowledge in order to provide additional
supportive evidence on
relevance of any
positive, negative, conflicting or inconclusive
prediction and
provide a rationale to
support the final conclusion.
如果可以得到保证的话,
所有基于计算机系统的分析均可以使用专家知识进行审核,
以对所
有阳性、
阴性、
相互矛盾或无法得出结论的预期之间的相关性提供额外的支持性证据,
从而
p>
支持最终结论的合理性。
To follow up on a relevant structural
alert (Class 3 in Table 1), either adequate
control
measures
could
be
applied
or
a
bacterial
mutagenicity
assay
with
the
impurity
alone
can
be
conducted.
An
appropriately
conducted
negative
bacterial
mutagenicity
assay
(Note
2)
would
overrule
any
structure-based
concern,
and
no
further
genotoxicity
assessments
would
be
recommended
(Note
1).
These
impurities
should
be
considered non-mutagenic
(Class 5 in Table 1). A positive bacterial
mutagenicity
result
would
warrant
further
hazard
assessment
and/or
control
measures
(Class
2
in
Table 1). For instance,
when levels of the impurity cannot be controlled
at an
appropriate
acceptable
limit,
it
is
recommended
that
the
impurity
be
tested
in
an
in
vivo
gene
mutation assay in order to understand the
relevance of the bacterial
mutagenicity
assay result under
in vivo
conditions. The selection of other
in
vivo
genotoxicity
assays
should
be
scientifically
justified
based
on
knowledge
of
the
mechanism of action of the impurity and expected
target tissue exposure (Note
3).
In vivo
studies should be
designed taking into consideration existing ICH
genotoxicity Guidelines. Results in the
appropriate
in vivo
assay
may support
setting compound specific
impurity limits.
在对有关的警示结构
p>
(表
1
第
3
类)
进行确认之后,
可以采用充分的控制措施
,或者对该杂
质单独进行细菌诱变测试。如果所得的细菌诱变测试(注
< br>2
)结果为阴性,则可以推翻基于
结构的疑虑,这时不建
议进行进一步的基因毒性评估(注
1
)。这些杂质应被当作非诱
变性
杂质(表
1
中第
< br>5
类)。如果细菌诱变测试为阳性,则要进行进一步的危害性分析和
/
或采
取控制措施
(表
p>
1
中第
2
类)
p>
。
例如,
如果杂质的水平不能被控制在一个
适当的可接受水平,
则建议进行体内基因诱变测试,
以搞清楚在
体内环境下细菌诱变测试结果。
其它体内基因毒
性测试的选择也
应根据杂质的反应机理和预期标靶组织暴露(注
3
)的知识进行
科学论述。
体内研究的设计应考虑已有的
ICH
基因毒性指南。
恰当的体内测试结果可以用于支持设定特
定化合物杂质的限度。
An impurity
with
a structural alert
that
is shared (e.g., same
structural alert
in
the same
position and chemical environment) with the drug
substance or related
compounds can be
considered as non-mutagenic (Class 4 in Table 1)
if the testing
of such material in the
bacterial mutagenicity assay was
negative.
如果一种杂质
具有与药用物质或相关化合物具有相似的警示结构
(例如,
在相
同位置和相同
化学环境下具有相同警示结构)
,
且该物料的细菌诱变测试为阴性,
则该杂质可以被认为是
非诱变性的(表
1
第
4
类)。
7. RISK
CHARACTERIZATION
风险定性
As a result
of hazard assessment described in Section 6, each
impurity will be
assigned
to
one
of
the
five
classes
in
Table
1.
For
impurities
belonging
in
Classes
1,
2,
and
3
the
principles
of
risk
characterization
used
to
derive
acceptable
intakes
are described in this
section.
作为第
6
部分所述的危害性评估的结果,
每个杂质会按表
1
中分在
5
类中。
本部分描述的是
用于
1
、
2
、
3
类杂质计算可接
受摄入量的风险定性原则。
7.1 TTC-based
Acceptable Intakes
根据
TTC
计算可接受摄入量
A
TTC-based
acceptable
intake
of
a
mutagenic
impurity
of
1.5
μ
g
per
person
per
day
is considered to be associated with a
negligible risk (theoretical excess cancer
risk of <1 in 100,000 over a lifetime
of exposure) and can in general be used for
most pharmaceuticals as a default to
derive an acceptable limit for control. This
approach
would
usually
be
used
for
mutagenic
impurities
present
in
pharmaceuticals
for
long-term
treatment
(>
10
years)
and
where
no
carcinogenicity
data
are
available
(Classes 2 and
3).
根据
TTC
< br>计算可接受摄入量时,一个具有诱变性的杂质每天每人摄入
1.5
μ
g
时其风险被认
为是可以忽
略的
(终生暴露情况下理论的患癌风险小于十万分之一)
,
p>
可以通用于大部分药
物,
作为默认的可接受
限度控制标准。
该方法一般用于长期治疗用药物中的诱变性杂质
(
>10
年),且没有致癌数据时(第
2
类和
3
类)。
7.2 Acceptable Intakes Based on
Compound-Specific Risk Assessments
根据化合
物
特定风险评估计算的可接受摄入量
7.2.1 Mutagenic Impurities with
Positive Carcinogenicity Data (Class 1 in Table
1)
具有阳性致癌数据的诱变杂质(表
1
第
1
类)
Compound-specific risk
assessments to derive acceptable intakes should be
applied
instead of the TTC-based
acceptable intakes where sufficient
carcinogenicity data
exist.
For
a
known
mutagenic
carcinogen,
a
compound-specific
acceptable
intake
can
be
calculated
based
on
carcinogenic
potency
and
linear
extrapolation
as
a
default
approach.
Alternatively,
other
established
risk
assessment
practices
such
as
those
used
by
international
regulatory
bodies
may
be
applied
either
to
calculate
acceptable
intakes
or
to
use
already
existing
values
published
by
regulatory
authorities (Note
4).
如果具备足够的基因致癌性数据,
则应采用对特定化合物进行风险评估的方式计算可接受摄
入量,
取代根据
TTC
所计算的可接受摄入量。
< br>对于已知具有突变致癌性的化合物,
可以根据
致癌可能性
和线性计算可接受摄入量,
这时默认采用线性外推法。
对应地,
其它已实施的风
险评估经验,例如,
被
国际法规实体采用的经验,
也可以用于计算可接受摄入量,
或采
用已
由法规当局公布的值(注
4
)。<
/p>
Compound-specific
calculations
for acceptable intakes can
be applied case-by-case
for
impurities which are chemically similar to a known
carcinogen compound class
(class-
specific
acceptable
intakes)
provided
that
a
rationale
for
chemical
similarity and
supporting data can be demonstrated (Note
5).
对特定化合物的可接受摄入量的计算方法可以根据实际
情况应用于与已知致癌化合物在化
学结构上类别较相似的杂质
(
按类别制订的可接受摄入量)
,
但前提是必须证明该杂质与已<
/p>
知化合物化学结构相似性的合理性及具备支持性数据。
7.2.2 Mutagenic Impurities with
Evidence for a Practical Threshold
有实际阈值
证据的诱变性杂质
The existence of mechanisms leading to
a dose response that is non-linear or has
a practical threshold is increasingly
recognized, not only for compounds that
interact with non-DNA targets but also
for DNA-reactive compounds, whose effects
may be modulated by, for example, rapid
detoxification before coming into contact
with
DNA,
or
by
effective
repair
of
induced
damage.
The
regulatory
approach
to
such
compounds
can be based on the identification of a No-
Observed Effect Level (NOEL)
and
use
of
uncertainty
factors
(ICH
Q3C(R5),
Ref.
7)
to
calculate
a
Permissible
Daily
Exposure (PDE) when data are
available.
大家现在越来越认识到,
有一些机理说明对剂量的反应并非线性或实用阈值,
不仅仅是与非
DNA
靶标产生作用的化合物,也包括与
DNA<
/p>
有活性反应的化合物,其影响可能会,例如,在
与
DNA
接触前其毒性即被快速清除,
或对产生的损伤进
行有效修复。
针对该类化合物的合规
方法可以是根据对无明显反
应水平(
NOEL
)的鉴别,
在可以获
得数据的情况下,使用不确定
性因子(
ICH Q3C
(
R5
)参考文献
7<
/p>
)计算允许日暴露量(
PDE
)。
The
acceptable
intakes
derived
from
compound-specific
risk
assessments
(Section
7.2)
can
be adjusted for shorter duration of use in the
same proportions as defined in
the
following sections (Section 7.3.1 and 7.3.2) or
should be limited to not more
than
0.5%, whichever is lower. For example, if the
compound specific acceptable
intake is
15
μ
g/day for lifetime
exposure, the less than lifetime limits (Table
2)
can
be
increased
to
a
daily
intake
of
100
μ
g
(>
1-10
years
treatment
duration),
200
μ
g (> 1-12
months)
or 1200
μ
g (< 1
month).
However, for a drug
with a maximum
daily dose of, for instance, 100 mg the
acceptable daily intake for the < 1 month
duration would be limited to 0.5% (500
μ
g) rather than 1200
μ
g.
在短
期服用时,
特定化合物风险分析所获得的可接受服用量
(第
p>
7.2
部分)
可以按以下部分
所指定的比例进行调整(第
7.3.1
和
7.3.2
部分),或限制不超过
0.1%
,取低者。例如,
如果一个特定化合物的可接受服用量为终生暴露期<
/p>
15
μ
g/
天,
在短于终生时长暴露时的限
度(表
2
)
可以增加至
100
μ
g
(
>1-10
年治疗进长),
200
μ
g
(
>1-12
月)或
1200
μ
g
(
<1
个月)。但是
,对于具有最大日服用剂量的药物,例如,
100mg
,则
p>
<1
个月时长的可接受日
服用剂量应受限于
0.1%
(
500
μ
g
),而不是
1200
μ
g
。
7.3 Acceptable Intakes in Relation to
LTL Exposure
与
LTL
暴露有关的可接受摄入
量
Standard risk assessments of known
carcinogens assume that cancer risk increases
as a function of cumulative dose. Thus,
cancer risk of a continuous low dose over
a lifetime would be equivalent to the
cancer risk associated with an identical
cumulative exposure averaged over a
shorter duration.
对已知致癌物的标准风险评估假定癌症风险随着给药量的累积而增加,
这样,
终生以低剂量
持续给药时癌症风险则与在短期内大量给药具有相同的累
积暴露平均值。
The TTC-based
acceptable intake of
1.5
μ
g/day is considered to
be protective for
a lifetime of daily
exposure. To address LTL exposures to mutagenic
impurities in
pharmaceuticals,
an
approach
is
applied
in
which
the
acceptable
cumulative
lifetime
dose (1.5
μ
g/day x
25,550 days = 38.3 mg) is uniformly distributed
over the total
number of exposure days
during LTL exposure. This would allow higher daily
intake
of mutagenic impurities than
would be the case for lifetime exposure and still
maintain comparable risk levels for
daily and non-daily treatment regimens. Table
2
is
derived
from
the
above
concepts
and
illustrates
the
acceptable
intakes
for
LTL
to
lifetime
exposures
for
clinical
development
and
marketing.
In
the
case
of
intermittent
dosing,
the
acceptable
daily
intake
should
be
based
on
the
total
number
of dosing days
instead of the time interval over which the doses
were administered
and that number of
dosing days should be related to the relevant
duration category
in Table 2. For
example, a drug administered once per week for 2
years (i.e., 104
dosing days) would
have an acceptable intake per dose of
20
μ
g.
基于
TTC
计算的可接受日摄入量
1.
5
μ
g/
天被认为是在终生每日暴露情
况下可以受到保护的
量。
在说明药品中诱变性杂质的
LTL
暴露量时,
所采用的方法是假定可接受的累
积终生剂量
(
1.5
μ
g/
天
X25,550
天
p>
=38.3mg
)
在终生摄入期间是均匀分
布在这些天数中的,
这样诱变性
杂质的日摄入量可以高于平均终
生日暴露量,
而其风险水平仍与每日或非每日治疗方案相持
平。
表
2
是从上述概念得到的数据,
其中写出了临床研发阶段和上市阶段终生暴露
LTL
< br>下可
接受摄入量数值。
如果给药是间歇性的,
则可接受日摄入量应根据给药总天数计算,
而不是
服用药物的总时间长度计算,给药天数与表
2
中相关时长分类有
关。例如,
2
年期间每周服
用一次的药
物(即
104
个服药天数),其可接受摄入剂量为每剂
20
μ
g
。
Table 2: Acceptable Intakes for
an Individual Impurity
Duration
treatment
Total
Daily
120
20
10
of
≤
1month
>1-12months
>1-10years
>10
years
to
lifetime
1.5
intake
(
μ
g/day)
表
2:<
/p>
单个杂质的可接受摄入量
治疗期
日总摄入量
(
μ
g/
天
)
≤
1
月
120
>1-12
月
20
>1-10
年
10
>10
年到终生
1.5
7.3.1 Clinical Development
临床研发
Using
this
LTL
concept,
acceptable
intakes
of
mutagenic
impurities
are
recommended
for limited
treatment periods during clinical development of
up to 1 month, 1 to
12
months
and
more
than
one
year
up
to
completion
of
Phase
3
clinical
trials
(Table
2). These adjusted
acceptable intake values maintain a 10-6
risk level in early
clinical
development
when
benefit
has
not
yet
been
established
and
a
10-5risk
level
for later stages in development (Note
6).
采用
LTL
概念,诱变性杂质
的可接受摄入量在临床研究中的治疗期限最高为
1
个月、
1-12
个月及长于
1
年直到完成
3
期临床试验(表
2
p>
)。对可接受摄入值的调节在其受益水平尚未
不可知时,保持早期临
床风险水平为百万分之一,后期临床为十万分之一。
An
alternative approach
to the strict use
of an
adjusted acceptable
intake for
any
mutagenic impurity could be applied for
Phase 1 clinical trials for dosing up to
14 days. For this approach, only
impurities that are known mutagenic carcinogens
(Class 1) and known mutagens of unknown
carcinogenic potential (Class 2), as well
as impurities in the cohort of concern
chemical class, should be controlled (see
Section
8)
to
acceptable
limits
as
described
in
Section
7.
All
other
impurities
would
be treated as non-
mutagenic impurities. This includes impurities
which contain
structural
alerts
(Class
3),
which
alone
would
not
trigger
action
for
an
assessment
for this limited
Phase 1 duration.
所有诱变性杂质经过
调整的可接受摄入量严格用法的替代方式可以应用于长达
14
天
的一期
临床试验阶段。采用该方法时,只有已知诱变性致癌(
1
类)杂质和致癌性未知的已知诱变
物(
2
类),以及被列入关注化学类别中的杂质要控制(参见第
8<
/p>
部分)在第
7
部分的可接
受限度内。所有其它杂质可以作为非诱变性杂质对待,其中包括含有警示结构(
3
类)的杂
质。仅仅只是含有警示结构不需要在一期临床试验期
间进行评估。
7.3.2 Marketed
Products
已上市药物
The treatment duration categories with
acceptable intakes in Table 2 for marketed
products
are
intended
to
be
applied
to
anticipated
exposure
durations
for
the
great
majority
of
patients.
The
proposed
intakes
along
with
various
scenarios
for
applying
those intakes are described in Table 4,
Note 7. In some cases, a subset of the
population of patients may extend
treatment beyond the marketed drugs categorical
upper limit (e.g., treatment exceeding
10 years for an acceptable intake of 10
μ
g/day,
perhaps
receiving
15
years
of
treatment).
This
would
result
in
a
negligible
increase (in the example given, a
fractional increase to 1.5/100,000) compared to
the overall calculated risk for the
majority of patients treated for 10 years.
已上市药品的治疗时长分类与可接受摄入量在表
2
中列
中。
它可以用来预计绝大部分患者的
暴露时长。
所拟的摄入量与使用这些摄入量的不同情景在表
4
注<
/p>
7
中已有说明。
在有些情况
下,患者中一部分人群可能会延长治疗时长,
超出上市药物分类的上限
(例如,可接受摄入
量为
10
μ
g/
天的药物治疗超出
10
年,可能会接受
15
年治疗)。与按绝
大部分患者治疗
10
年计算出的整体风险相比,
延长治疗时长导致的风险增加
(如上例,
增加比例为<
/p>
1.5/100000
)
可以忽略。
p>
7.4 Acceptable Intakes for
Multiple Mutagenic Impurities
多个诱变性杂质可接受
摄入量
The
TTC-based
acceptable
intakes
should
be
applied
to
each
individual
impurity.
When
there are two Class 2
or Class 3 impurities, individual limits apply.
When there
are three or more Class 2 or
Class 3 impurities specified on the drug substance
specification, total mutagenic
impurities should be limited as described in Table
3 for clinical development and marketed
products.
根据
TTC<
/p>
制订的可接受摄入量要用单独应用于各个杂质。
如果有两个
2
类或
3
类杂质,<
/p>
则限
度是针对单个杂质的。
如果原料药质
量标准中有
3
个或更多
3
类或
3
类杂质,
临床研发和
已
上市药品中的总诱变性杂质应根据表
3
所列进行限制。
For combination
products each active ingredient should be
regulated separately.
对于复方药品,每个活性成分要分别规定。
Table 3: Acceptable Total Daily Intakes
for Multiple Impurities
Duration
treatment
Total
intake
(
μ
g/day)
表
3:
多个杂质的可接受日总摄入量
治疗期
日总摄入量
(
μ
g/
天
)
Only specified
Class 2 and 3 impurities on the drug substance
specification are
included
in
the
calculation
of
the
total
limit.
However,
impurities
with
compound-specific or
class-related acceptable intake limits (Class 1)
should not
be
included
in
the
total
limits
of
Class
2
and
Class
3
impurities.
Also,
degradation
products
which
form
in
the
drug
product
would
be
controlled
individually
and
a
total
limit would not be applied.
在原料药质量标准中,
只有列出的
2
类
和
3
类杂质才会被包括在总限度计算中,
而特定化合
物或按可接受摄入限度分类(第
1
类)的杂质不应计入第
2
类和第
3
类杂质总限度。还有,
原料药中形成的降解产物要单独控制
,不能计入总限度。
7.5 Exceptions and
Flexibility in Approaches
方法特例和灵活性
≤
1
月
120
>1-12
月
60
>1-10
年
30
>10
年到终生
5
Daily
120
60
30
of
≤
1month
>1-12months
>1-10years
>10
years
to
lifetime
5
? Higher acceptable intakes may be
justified when human exposure to the impurity
will
be
much
greater
from
other
sources
e.g.,
food,
or
endogenous
metabolism
(e.g.,
formaldehyde).
如果人们暴露于其它杂质其它来源,
如,
食品或内源
性代谢物
(例如甲醛)
的可能性非常
大,则可以考虑判定较高的可接受摄入量。
? Case-by-case exceptions to the use of
the appropriate acceptable intake can be
justified
in
cases
of
severe
disease,
reduced
life
expectancy,
late
onset
but
chronic
disease, or with
limited therapeutic alternatives.
使用适当的
可接受摄入量可以用于以下各案例外情况:
病情严重、
降低生命
期望、
发病迟但
长期疾病,或其它治疗方法有限的情况。
? Compounds from some
structural classes of mutagens can display
extremely high
carcinogenic potency
(cohort of concern), i.e., aflatoxin-like-,
N-nitroso-, and
alkyl-azoxy
structures.
If
these
compounds
are
found
as
impurities
in
pharmaceuticals,
acceptable
intakes
for
these
high-potency
carcinogens
would
likely
be
significantly lower than the acceptable intakes
defined in this guideline.
Although
the
principles
of
this
guideline
can
be
used,
a
case-by-case
approach
using
e.g., carcinogenicity data from closely
related structures, if available, should
usually be developed to justify
acceptable intakes for pharmaceutical development
and marketed products.
有些诱变结
构类别的化合物可能会显示出非常高的诱变性
(关注的队列),例如,黄曲霉毒
素类、
N-
亚硝基化合物、以及烷基
-
氧化偶氮结构。如果在药物的杂质中存在杂质是这样的
< br>化合物,
则这些高效价诱变物的可接受摄入量很可能要显著低于本指南中定义的可
接受摄入
量。尽管如果,也还是能使用本指南的原则,一般要研究一种针对各案采用,例
如,已有的
近似的相关结构的基因致癌数据,的方法来判定药品研发和上市药品中的可接
受摄入量。
The above risk
approaches described in Section 7 are applicable
to all routes of
administration and no
corrections to acceptable intakes are generally
warranted.
Exceptions to consider may
include situations where data justify route-
specific
concerns
that
should
be
evaluated
case-by-case.
These
approaches
are
also
applicable
to
all
patient
populations
based
upon
the
conservative
nature
of
the
risk
approaches
being applied.
p>
在第
7
部分中所描述的上述风险方法可以应
用于所有摄入途径,不需要修正可接受摄入量。
对例外情况的考虑可能包括需要各案评价
的特定摄入途径数据判定。
由于所采用的风险方法
是较为保守的
,因此这些方法也适用于所有患者人群,
8.
CONTROL
控制
A
control strategy is a planned set of controls,
derived from current product and
process
understanding
that
assures
process
performance
and
product
quality
(ICH
Q10,
Ref. 8). A control strategy can
include, but is not limited to, the following:
控制策略是指从现行产品和工艺知识中获得的,
保证工艺性能和产品质
量的一套有计划的控
制方法。一个控制策略可以包括,但不限于以下:
< br>
—
Controls
on
material
attributes
(including
raw
materials,
starting
materials, intermediates, reagents,
solvents, primary packaging materials);
—
p>
物料特性控制(包括原料、起始物料、中间体、试剂、溶剂、内包材)
—
Facility and equipment operating
conditions;
—
设施和设备操作条件
—
Controls implicit in the design of the
manufacturing process;
—
生产工艺设计中的控制内涵
—
In-process
controls
(including
in-process
tests
and
process
parameters);
—
中控(包括中控检测和工艺参数)
—
Controls
on
drug
substance
and
drug
product
(e.g.,
release
testing).
—
原料药和制剂控制(例如,放行检测)
When an impurity has been
characterized as Classes 1, 2, or 3 in Table 1, it
is
important
to
develop
a
control
strategy
that
assures
that
the
level
of
this
impurity
in the drug
substance and drug product is below the acceptable
limit. A thorough
knowledge
of
the
chemistry
associated
with
the
drug
substance
manufacturing
process,
and of the drug
product manufacturing process, along with an
understanding of the
overall
stability
of
the
drug
substance
and
drug
product
is
fundamental
to
developing
the
appropriate
controls.
Developing
a
strategy
to
control
mutagenic
impurities
in
the
drug
product
is
consistent
with
risk
management
processes
identified
in
ICH
Q9
(Ref.
9).
A
control
strategy
that
is
based
on
product
and
process
understanding
and
utilisation of risk
management principles will lead to a combination
of process
design and control and
appropriate analytical testing, which
can also provide an
opportunity
to
shift
controls
upstream
and
minimize
the
need
for
end-product
testing.
如果一个杂质已根
据表
1
进行了定性分类为
1
、
2
或
3
类,则研究一种控制策略来保证该杂
质在原料药和制剂中存在的水平低于可接受
限度是很重要的。
在建立适当的控制策略时,
对
原料工生产工艺的化学方面的深入理解、
对制剂生产工艺的了解、
对原料药和制剂全面稳定
性的了解是很必要的。
建立
一种策略来控制原料药中的诱变性杂质是与
ICH
Q9
(参考文献
9
)
中定
义的风险管理过程相一致的。
控制策略应该是根据对产品和工艺的理解,
利用风险管理
原则进行综合的工艺设计和控制,
以及适
当的分析检测。
这也能提供一个机会来转移对上游
进行控制,并
将最终产品检测的必要性降至最小。
8.1 Control
of Process Related Impurities
工艺相关杂质的控制
There
are 4 potential approaches to development of a
control strategy for drug
substance:
有
4
种方法可供选择用作原料药控制策略:
Option 1
第
1
种方法
Include
a
test
for
the
impurity
in
the
drug
substance
specification
with
an
acceptance
criterion
at
or
below
the
acceptable
limit
using
an
appropriate
analytical
procedure.
在原料药质
量标准中加入杂质检测并制订质量标准,
标准不高于采用适当的分析方法时的可
接受限度。
For an Option 1
control approach, it is possible to apply periodic
verification
testing per ICH Q6A (Ref.
10). Periodic verification testing is justified
when it
can be shown that levels of the
mutagenic impurity in the drug substance are less
than 30% of the acceptable limit for at
least 6 consecutive pilot scale or 3
consecutive
production
scale
batches.
If
this
condition
is
not
fulfilled,
a
routine
test
in
the
drug
substance
specification
is
recommended.
See
Section
8.3
for
additional
considerations.
根据
ICH
Q6A
(参考文献
< br>10
),方法
1
控制方式可以适
用定期检测。如果原料药中的诱变
性杂质在至少
6
个连续的中试批次或
3
个连续的生产批次中,
测得结果均低于可接受限度的
30%
,则可以
论述进行定期检测。如果不满足该条件,则建议对原料药进行常规检测。参见
8.3
p>
中更多考虑因素。
Option 2
第
2
种方法
Include a test for the impurity in the
specification for a raw material, starting
material
or
intermediate,
or
as
an
in-process
control,
with
an
acceptance
criterion
at or below the acceptable limit using
an appropriate analytical procedure.
p>
在原料、
起始物料或中间体的质量标准中包括对杂质的检测,
或作为中控检测,
同时制订可
接受标准,或采
用适当的分析方法,将杂质控制在可接受限度以下。
Option 3
第
3
种方法
Include a test for the impurity in the
specification for a raw material, starting
material
or
intermediate,
or
as
an
in-process
control,
with
an
acceptance
criterion
above
the
acceptable
limit
of
the
impurity
in
the
drug
substance,
using
an
appropriate analytical
procedure coupled with demonstrated understanding
of fate
and
purge
and
associated
process
controls
that
assure
the
level
in
the
drug
substance
is
below the
acceptable
limit
without the need for any additional testing later
in
the process.
在原料、
起始物料或中间体的质量标
准中包括对杂质的检测,
或作为中控检测,
同时制订一
个高于原料药中可接受限度的质量标准,
采用适当的分析方法,
配合经过证明杂质致命知识,
杂质在后续工艺中被清除的知识,
并对后续工艺进行控制,
保证原料药中的该杂质残留水平
低于可接受限度,而不需要在后续工艺中再行检测。
This option can be justified when the
level of the impurity in the drug substance
will
be
less
than
30%
of
the
acceptable
limit
by
review
of
data
from
laboratory
scale
experiments (spiking experiments are
encouraged) and where necessary supported by
data from pilot scale or commercial
scale batches. See Case Examples 1 and 2.
Alternative approaches can be used to
justify Option 3.
当实验室级试验
(鼓励采用加样试验)
数据,
必要时可以采用
中试生产或商业批次数据加以
支持,显示原料药中杂质水平低于可接受限度的
30%
时,可以采用该方法。
Option 4
第
4
种方法
Understand
process
parameters
and
impact
on
residual
impurity
levels
(including
fate
and purge knowledge)
with sufficient confidence that the level of the
impurity in
the
drug
substance
will
be
below
the
acceptable
limit
such
that
no
analytical
testing
is recommended for this impurity.
(i.e., the impurity does not need to be listed
on any specification).
对工艺参数和残留杂质水平
(包括致命性和清除知识)
影响有了解,
确信原料药中的杂质一
定会低于可接受限度,
此时,建议该杂质不需要进行分析测试
(例如,
不需要将杂质列
在任
何质量标准中)。
A
control strategy that relies on process controls
in lieu of analytical testing
can
be
appropriate
if
the
process
chemistry
and
process
parameters
that
impact
levels
of mutagenic
impurities
are understood and the risk
of an impurity residing in the
final
drug
substance
above
the
acceptable
limit
is
determined
to
be
negligible.
In
many cases justification of this
control approach based on scientific principles
alone
is
sufficient.
Elements
of
a
scientific
risk
assessment
can
be
used
to
justify
an
option
4
approach.
The
risk
assessment
can
be
based
on
physicochemical
properties
and process
factors that influence the fate and purge of an
impurity including
-
-
-
-
-
-
-
-
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