Full Text
EXTRAORDINARY
PART III—Section 4
PUBLISHED BY AUTHORITY
No. 9 96] NEW DELHI, TUESDAY , DECEMBER 17, 2024 /AGRAHAYAN 26, 194 6
CG-DL-E-17122024-259484
(m/s)
Tier 1 -
•
•
•
•
•
•
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Tier 2 -
10 THE GAZ ETTE OF INDIA : EXTRAORDINARY [PART III—SEC.4]
Tier 3 -
(2)
(3)
14 THE GAZE TTE OF INDIA : EXTRAORDINARY [PART III—SEC.4]
= 1200/40*0.386 = 11.5 महीने
(4)
(5)
)6)
16 THE GAZE TTE OF INDIA : EXTRAORDINARY [PART III—SEC.4]
(8)
(m/s)
18 THE GAZE TTE OF INDIA : EXTRAORDINARY [PART III—SEC.4]
(9)
20 THE GAZE TTE OF INDIA : EXTRAORDINARY [PART III—SEC.4]
उपयोग IIC 10- 70 H3 – H6
(11)
22 THE GAZE TTE OF INDIA : EXTRAORDINARY [PART III—SEC.4]
(12)
24 THE GAZE TTE OF INDIA : EXTRAORDINARY [PART III—SEC.4]
26 THE GAZE TTE OF INDIA : EXTRAORDINARY [PART III—SEC.4]
28 THE GAZE TTE OF INDIA : EXTRAORDINARY [PART III—SEC.4]
NATIONAL DAM SAFETY AUTHORITY
NOTIFICATION
New Delhi, the 5th December , 2024
F. No. TE -32/2/2023 -NDSA -MOWR .—In exercise of the powers conferred by sub -section (1), read with
clause ( b) of sub -section (2) of section 54 of the Dam Safety Act, 2021 (41 of 2021), the National Dam Safety Authority,
on the recommendations of the National Committee on Dam Safety, hereby makes the following regulations, namely: -
1. Short title and c ommencement . – (1) This regulation may be called the Vulnerability and Hazard Classifications
of Dams Regulations, 2024.
(2) This shall come into force on the date of its publication in the Official Gazette.
2. Definitions. - (1) In this regulation , unless the context otherwise requires, -
(a) “Act” means the Dam Safety Act, 2021(41 of 2021);
(b) “Authority” means the National Dam Safety Authority established under section 8 of the Act;
(c) “hazard” means a dangerous condition or event, that threat or have the potential for causing injury to life or damage to
the property or the environment ;
(d) “ hazard potential” means the downstream damage that may result if the dam were to fail ;
(e) “risk” means a measure of the likelihood and severity of adverse consequence, which is estimated by the
mathematical expectations of the consequence of an adverse event occurring i.e. the product of the probability of
occurrence and consequence;
(f) “section” means a section of the Act.
(g) “vulnerability” means the relative risk associated with the dams, on the basis of their condition, location and damage ;
(2) Words and expressions used herein and not defined in these regulations but defined in the Act , shall have the
meanings respectively , assigned to them in the Act.
3. Criteria for vulnerability and hazard classification of a dam - (1) The State Dam Safety Organization shall classify
each dam under their jurisdiction as per the following, namely: -
(i) Category -I: Deficiencies in dams which, if left unattended, may lead to failure.
(ii) Category -II: Major deficiencies requiring prompt remedial me asures.
(iii) Category -III: None or minor deficiencies which are rectifiable.
(2) The v ulnerability classification shall be carried out in accordance with sub-para (c) of Part 2 of Schedule -I of the
Inspection, Instrumentation, Seismic Data, Risk Assessment and Evaluation of Specified Dam Regulation, 2024 .
(3) The c riteria of hazard classification shall be as following, namely: -
(i) Dam hazard classification shall be based on an “additive weighting” and “point index ” and aggregates the assessment
of the consequences in four major categories that is the capital value of the project, potential for loss of life, the potential
for property damage and Potential for Environmental and Cultural impact.
(ii) hazard potential is categorized into four classes as specified in the Table-1 below based on the consequences
category:
Table 1 - Consequences Categories in the Dam Classification
Hazard
Potential
Class Consequences Categories
Capital
Value of
Project Potential for Loss of Life Potential for Property
Damage Potential for
Environmental and
Cultural Impact
Class I Low None. Occasional or no
incremental population at risk,
no potential loss of life is
expected. No inhabited
structures. Minimal. Limited
economic and
agricultural
development. None
Class II Average Minimal or low population at
risk. No potential loss of life is
expected even during the worst -
case scenario of emergency
management . Notable agriculture or
economic activities.
States h ighways and
rail lines. Minimal incremental
damage. Short -Term or
reversible impact (less
than 2 years) .
Class III Significant Considerable. Several inhabited
developments. Potential for loss
of life highly dependent of the
adequacy of warning and rescue
operations. Significant industry,
commercial and
economic
developments. National
and state highways and
rail lines. Limited. Impact have a
mid-term d uration (less
than 10 years) with
high probability of total
recovery after
mitigation measures .
Class IV Critical Extreme. High density populated
areas. Potential for loss of life is
too high even during the best
scenario of emergency
management . Highly developed area
in terms of industry,
property, transportation
and lifeline features . Severe. Long -term
impact/effects in the
protected areas or
cultural heritage sites
with low probability of
recovery.
4. Failure Scenario for the Dam Hazard Classification - (1) The hazard potential classification assigned to a dam is
based on consideration of the effects of failure or mis -operation during both normal and flood flow conditions.
(2) The classification assigned sh all be based on the worst -case scenario of failure or m is-operation of the dam, i.e., the
assigned classification sh all be based on incremental failure consequences that will result in the assignment of the
highest hazard potential classification of all probable failure and mis operation scenarios.
(3) Each e lement of a project shall be evaluated to determine the proper hazard potential classification for the project.
(4) O nly one hazard potential classification shall be assigned to the entire project and i ndividual elements are not
assigned separate classific ations.
5. Vulnerability or severity assessment . – (1) The degree of hazard shall vary with the severity of flooding and is
affected by the flood and its hydraulic behaviour (extent, depth, velocity, duration and rate of rising of the floodwaters),
the topography, population at risk and emergency management.
(2) Once the flood hazard of the dam event (failure scenarios) has been quantified, the potential of the flood flows to
cause damage or danger shall be indexed against vulnerability curves linked to meaningful hazard thresholds.
(3) The vulnerability of the d ownstream community and its assets shall be described by using thresholds related to the
stability of people as they walk or drive through flood waters, or shelter in a building during a flood.
(4) The vulnerability to hazard shall also be influenced by the primary consideration of strategic land -use planning, which
is aimed at ensuring land use is compatible with the flood risk or assessing development proposals or emergency
management planning, which is aimed at addressing residual flood risks.
(5) A flood severity assessment conducted as part of a dam hazard classification process shall provide information to
identify those consequences with the highest significance among the entire floodplain.
(6) A combined set of hazard curves (vulnerabilit y of people, vehicles and buildings) are given at Table 2 and Figure 1
below: -
Table 2 - Vulnerability thresholds classification limits a
Hazard
Vulnerability
Classification Description Classification
Limit
(Depth *
Velocity) Limiting
Water
Depth
(m) Limiting
Velocity
(m/s)
H1 Generally safe for vehicles, people and
buildings. D*V < 0.3 0.3 2.0
H2 Unsafe for small vehicles. D*V < 0.6 0.5 2.0
H3 Unsafe for vehicles, children and the
elderly. D*V < 0.6 1.2 2.0
H4 Unsafe for vehicles and people. D*V < 1.0 2.0 2.0
H5 Unsafe for vehicles and people. All
buildings are vulnerable to structural
damage. Some less robust buildings
subject to failure. D*V < 4.0 4.0 4.0
H6 Unsafe for vehicles and people. All
building types considered vulnerable to
failure. D*V > 4.0 - -
a Combined Hazard – Vulnerability Classification (Smith et al., 2014)
Figure 1 - Flood Hazard Vulnerability Curves (Smith et al. 2014)
6. Limits of the Study Area . – (1) In order to establish the limits of the study area for a consequences assessment the
following aspects shall be considered and verified in the dam break analysis, which may help to delimit the boundaries of
the model . -
(a) no downstream presence of dwellings, services and other infrastructures ;
(b) no future developments are expected downstream of the boundaries of the model ;
(c) full attenuation of the breach outflow hydrograph along the main river ;
(d) channel -conveyance capacity of the mainstream (within the riverbanks) receiving the total outflow in the
downstream end of the model ;
(e) The existence of a downstream dam having a reservoir that lies within the downstream limits of the hydraulic
model of the upstream dam, which is either able or unable to absorb the total outflow hydrograph due to the dam
breach upstream and in case the reservoir located downstream is not able to absorb the entire volume received
from the upstream dam’s breach flood, a cascade failure effect sh all be scrutinized and i f a high likelih ood of
failure is corroborated for the downstream dam the downstream limits shall be extended ;
(2) The i nvestigation of the impact of failure or mis -operation of a dam on downstream human life, property damage,
lifeline disruption, and environmental concer ns shall be sufficient to determine the appropriate hazard potential
classification :
Provided that if failure or mis -operation of a dam leads to the failure of a downstream dam , the hazard potential
classification of the dam sh all be at least as high as the classification of the downstream dam and sh all consider the
adverse incremental conse quences of the domino failures.
7. Data requirement s. – (1) The a ssessment of consequences requires information on the effects of a potential dam
break, to provide the basis for the level as considered appropriate which includes data on dam and reservoir, topography ,
flood characteristics and inundation maps, information about the community residing in the downstream area,
implications for service and business, and implications to objects of strategic or national importance.
(2) Dam and reservoir data shall include information on dam type, dimensions of the dam such as height, width, and
length, spillway characteristics including gates and secondary spillways, relationship showing the reservoir elevation
versus storage volume, together with spillway discharge capacity up to the dam crest and comments on design,
foundations and unusual conditions as well as available repor ts on the design, construction, and management of the dam
and information on past incidents .
(3) (i) Topographic data shall cover the river sections where the depth and velocities of the flow may cause harm to life
or damage the property and the information sh all indicate the shape and slope of the valley and, when possible, the
structures or surfaces influencing on the downstream flow (e.g., culverts, weirs, bridges, levees, embankments, temporary
storage, floodplains, vegetation and other objec ts affecting the water surface elevations) ;
(ii) Topographic data shall also determine the boundary limits of the hydraulic model of the dam break analysis which is
enough to represent the entire downstream consequences and shall also include the location of major downstream
tributaries that may cause concurrent flooding ;
(iii) Channel cross -sections sh all be taken at regular intervals along the flood channel and a dditional sections may be
obtained for areas with a change in the channel profile such as restriction in section profile, like a bridge, confluence of
tributaries to the main channel and places with a significant change in the grade or cross -section of the channel ;
(iv) For the dam classification process, the level of detail s of the to pography or corresponding digital elevation model
(DEM) sh all be consistent, as a minimum, to a tier -I assessment.
(4) Information on flood characteristics and inundation maps shall include details about historical flood levels and flood
studies based on hydrographic data, as well as results from rainfall run -off modelling pertaining to different return
periods which also contain results of dam -break flooding under overtopping and non -overtopping conditions and shall
include travel times of flood waves to downstream locations of habitations .
(5) Information about the community residing in the downstream area shall include .-
(i) location, size and type of areas with human settlements within the possible area of inundation, the vulnerability of
various elements of the downstream community and the warning time available ;
(ii) details about awareness and flood preparedness of the downstream community and their temporal variation pattern
concerning days of the week and months and seasons ;
(iii) description of the areas identified for future development along with the land use classes and areas with toxic
substances, and the information on the infrastructure that may be affected (e.g., transport, power lines, water supply and
sewerage lines, gas pipes etc.).
(6) Implications of the dam break consequences for service and business shall include the importance of the water storage
to the business (e.g., municipal water supply, irrigation or hydropower generation), financial overburden , to meet the
costs of failure and the value of water in the storage reservoir.
(7) Implications to objects of strategic or national importance include inundations of areas which shall have
consequences of national significance like an inundation of a nuclear power plan t or a thermal power plant, or places
which if inundated will pose a threat to the national security , and may also include important historical structures or
biodiversity reserves or both.
8. Tiered assessment of Inundated Area and Flood Water Levels. - (1) With due considerations of the time
requirement and cost of detailed studies required to delineate areas which shall be inundated by a dam breach f lood,
tiered approach shall be taken to produce dam-breach inundation zone maps.
(2) The level of analysis for the tiered approach shall correlate with the sophistication and accuracy of the analys is with
the scale and complexity of the dam and downstream area under investigation, as per Table 3 .
(3) For Dam Hazard Classification process , a Tier -I analysis as specified in Table 3 shall be considered and adopted in
the following cases, namely: -
(a) dams which, due to their particular location and own characteristics, m ay be directly inferred as “low hazard”
and a Tier - I analysis sh all confirm the “low hazard” hypothesis ;
(b) as the first estimation for any high hazard dam under analysis and i f the results obtained through a Tier-I
analysis are enough to classify the specified dam under the highest hazard class, no further refinement would
be required in the classification process ;
(c) for any specified dam, irrespective of its “hazard”, only if the results from a Tier -I analysis ar e reliable enough
to conclude that further refinements shall not introduce changes in the hazard classification.
(4) A higher level of complexity in the consequence’s estimation (i.e. Tier – II and III) shall be introduced for the
classification process i n the following cases , namely: -
(a) consequences index (scoring points) obtained through a Tier -I analysis set the Hazard Class near the boundary
or threshold of a higher or lower hazard category ;
(b) better estimate in the population at risk assessment shall be ensured since it is considered as the critical
indicator in the hazard classification process of the specified dam ;
(c) clearer estimates in the flood severity assessment are desired for the consequences’ evaluation, which shall
make the use of a two -dimensional model .
9. Estimating population at risk. – (1) The population at risk shall include persons directly exposed to flood waters if
they are not evacuated , and a fter the delineation of the area inundated due to dam breach, estimation of the population at
risk may be carried out.
(2) It sh all be estimated using demographic data with occupancy rates for residences, number of students at schools,
number of persons in industrial, hospital, commercial and retail areas.
(3) The population at risk estimates may vary according to the time of day, the day of the week and month or season and
it is necessary to prepare more than one estimate and select the highest of these for determination of the consequence
category of the dam.
(4) It is important to consider the visitors to the recreational sports, camps, concert halls, parks and gardens as also those
who are driving through the roads or taking a railroad journey which gets inundated due to a dam break flood.
(5) The incremental analysis shall be taken into consideration for the estimation of population at risk and the rest of the
consequen ces.
10. Assessing potential damages and losses . – (1) The potential damages and losses due to a dam break may be grouped
into classes, including consequences of similar nature for the purpose of risk assessment which includes total
infrastructure costs, losses accrued due to the dam not being able to serve the purposes it is meant to, health and social
impacts, and the environmental impacts.
(2) Damages and losses may be classified as direct or indirect and d irect damages and losses comprise , those losses ,
which result from contact with the floodwaters and i ndirect damages and losses encompass all other damages and losses.
(3) The severity of each of these damages and losses may be either minor, medium, major or catastrophic which may be
established for each group of damage or loss, and summarised to the overall level of severity, with due consideration to
the regional or national economic perspective.
11. Assessment of health and social impacts . – The assessment of health and social impact shall be assessed on the
following parameters , namely : -
(a) the effects of dam break on health and social affairs shall depend on the nature, location, and extent of the area
affected by the dam failure, with regards to the distribution of the human habita tion;
(b) consumption of polluted drinking wate r or food due to contamination of the source or supply network which
may be due to failure or shortage of water, sewage, power supplies and u ncontrolled release of sewage,
industrial or toxic waste as a result of a dam break which may lead to widespread contamination ;
(c) social impacts of dam break shall depend on demographic characteristics, social and community values, needs
and networks, the extent of community support services, the capacity of respondin g institutions as well as the
degree of disaster preparedness and warning time available.
12. Consideration of Future Developments. - The consequence classification for a dam shall reflect the current
downstream development as well as the future developmen t plans.
Table 3 - Tiered approach to dam breach inundation mapping
Tier Level Applications Topography
/Bathymetry Breach
Parameter
Prediction Handling of the
Dam Breach
Parameters’
Uncertainty Peak Breach
Discharge Prediction Downstream
Routing of Breach
Outflow
Hydrograph Downstream Risk
Evaluation
Tier 1 –
Basic level
screening and simple
analysis • Hazard Classification
Process
• First level screening
for significant or high
hazard dams
• Low hazard potential
dams Low resolution terrain
data (e.g., SRTM,
ASTER, or ALOS),
with maximum 30 m
resolution. No
bathymetry required Empirical
formulae • Engineering
Judgmen t
• Reasonableness
of the peak
breach discharge
and velocities Empirical formulae
if inflow design
flood hydrograph is
not available,
otherwise unsteady
flow routing through
modelled reach HEC -RAS, MIKE or
similar one
dimensional (1D) or
two dimensional
(2D) unsteady flow
numerical models Peak discharge,
water surface
elevation,
depth*velocity and
flood wave travel
time
Tier 2 –
Intermediate level of
analysis • Large significant
hazard dams
• All high hazard dams Medium resolution
terrain data (e.g., 10 - 15
m resolution,
CartoDEM1) and
elevations adjusted
through ground control
points (GCPs).
Bathymetry required Empirical
formulae • Reasonableness
of the peak
breach discharge
• Sensitivity
analysis Unsteady flow
routing through
modelled breach HEC -RAS, MIKE or
similar two
dimensional (2D)
unsteady flow
numerical models
considering the
bathymetry Peak discharge,
water surface
elevation,
depth*velocity,
flood wave travel
time, and
approximate PAR
assessment
Tier 3 –
Advanced level of
analysis • Significant hazard
dams with complex
downstream flooding
• High hazard dams
with large population
at risk (PAR) High resolution terrain
data (Lidar, ALSO
enhanced) minimum 5
m resolution. Ground
control points (GCPs)
required.
Bathymetry required Empirical
equations,
physically
based models
(one or two
dimensional) • Probabilistic
Analysis (Monte
Carlo simulations
or similar
methods) Unsteady flow
routing through
modelled breach Coupled one -two
dimensional (1D -
2D) unsteady flow
numerical model.
Bathymetry also
considered Peak discharge,
water surface
elevation,
depth*velocity,
flood wave travel
time, and detailed
PAR assessment
13. Hazard Classification for dams. – (1) Hazard classification aggregates the assessment of the consequences in
following major categories, namely: -
(a) the capital value of project shall include the capital value of the project’s elements which may be destroyed
or damaged, and the loss of benefits, services, revenues provided by the dam project.
(b) the potential for loss of life be estimated indirectly through the estimation of the total population at risk in
the downstream areas and this category shall also consider the severity of the breach or failure flood if the
quality or type of modelling meets some standards, and the approximate arrival time of the flood wave (to
the closest and affected populated area), which is an indirect measur e of the available warning time;
(c) the p otential for property damage shall include the amount of damage to residential and commercial
property, agricultural lands, transportation facilities such as roads and bridges, damage and disruption of
lifeline and community service facilities ;
(d) the potential for enviro nmental and cultural impact shall i nclude the amount of damage to protected areas in
the country (wildlife sanctuaries, forest reserves, etc.) as well as potential impact to infrastructures of
cultural heritage or national importance.
(2) The detailed desc ription s of all categories for each of the four hazard classes are specified in Table 4.
(3) ( a) the additive weighting or point index scheme employs numerical ratings of the consequences which reflect the
relative importance of each consequence and the range of severity of the impacts ;
(b) the summation of the rating points from each consequence shall be used to establish the characteristics of the
consequences of failure of a given dam ;
(c) the overall categories and indicators used in the hazard potential classification for dams are specified in Table 5.
Table 4: Dam Classification based on the Additive weighting Scheme (Potential Consequences Index)
Hazard
Potential
Class Potential
Conseque
nces Index
(PCI)* Consequences Categories
Capital
Value of
Project Potential for Loss of Life Potential for Property
Damage Potential for
Environmental and
Cultural Impact
Class I < 300 Low None. Occasional or no incremental
population at risk, no potential loss
of life is expected. No inhabited
structures. Minimal. Limited
economic and
agricultural
development. None
Class II < 300 Average Minimal or low population at risk.
No potential loss of life is expected
even during the worst -case scenario
of emergency management Notable agricult ure or
economic activities.
States highways
and/or rail lines. Minimal incremental
damage. Short -Term or
reversible impact (less
than 2 years)
Class III 300 < P CI <
600 Significant Considerable. several inhabited
developments. Potential for loss of
life highly dependent of the
adequacy of warning and rescue
operations. Significant industry,
commercial and
economic
developments.
National and state
highways and rail
lines. Limited. Impact have a
mid-term d uration (less
than 10 years) with high
probability of total
recovery after mitigation
measures
Class IV > 600 Critical Extreme. High density populated
areas. Potential for loss of life is too
high even during the best scenario
of emergency management Highly developed
area in terms of
industry, property,
transportation and
lifeline features Severe. long -term
impact/effects in the
protected areas or
cultural heritage sites
with low probability of
recovery.
* Disclaimer: Dams with total consequences index near the boundaries between two classes (+/ - 50 points) warrant a
comprehensive assessment and additional engineering judgment to determine t he actual hazard classification
Table 5 - Numerical Rating Points a nd Categories for Assessing Consequences
Consequences
Category Indicator Parameter Consequences
Rating Points (min -
max) Considerations
Capital Value of
Project Dam Height 20 -100 Revenue Generation or Value of Reservoir
Content depending upon the reservoir
purpose (water supply, irrigation,
hydropower, etc.) Project Benefits 0-300
Potential for
Loss of Life Population at Risk 20-600 Incremental Population at Risk under higher
flood severity areas.
Minimum arrival of the breach/flood wave to
the nearest populated area downstream of the
dam Critical Arrival Time 0- 100
Potential for
Property
Damage Infrastructures
Damaged 0- 330 Residential and Commercial Properties
Roads, Bridges, Transportation Facilities
Lifeline Facilities and Community Services Services Disrupted 0-185
Potential for
Environmental
impact Environmental
Impact 0 - 200 Protected Areas and Cultural infrastructures
of National importance under higher flood
severity areas
Cultural Heritage 0 - 140
(a) Capital Value of Project
(1) It shall include the capital value of the project’s elements which shall be destroyed or damaged, and the loss of
benefits, services, revenues provided by the dam project .
(2) The two parameters namely: - Dam Height Index and Project Benefits Index shall be used for assessment of
capital value of project ,-
A. Dam height index
(i) Dam height may be considered as indicative of the capital value of a dam.
(ii) Consequence rating points corresponding to dam height index shall be calculated by the utility curve as
specified in Figure 2.
Figure 2 - Consequences Rating Points for Dam Height Index (I DH)
Alternatively, the index can be computed numerically according to the following formula:
𝑰𝑫𝑯
{ 𝟐𝟎,(𝒇𝒐𝒓 𝒉≤𝟓)
𝟏𝟓.𝟕+ 𝟏.𝟏𝟐∗[𝑳𝑵(𝒉)]𝟐.𝟖𝟐𝟗𝟐,(𝒇𝒐𝒓 𝟓<ℎ<𝟏𝟎𝟎) (1)
𝟏𝟎𝟎 ,(𝒇𝒐𝒓 𝒉 ≥𝟏𝟎𝟎)
Where ,-
IDH : Dam height index points, and
h : is the height of the dam in meters
B. Project benefits index. -
(i) Project benefits index (I PB) shall be estimated us ing the following subcategories , namely :- reservoir content
or water supply index (I RES), irrigation index (I I), hydropower generation index (I HP), and industrial use
index (I IU), and accordingly the total project benefits index can be calculated as follows:
IPB=IRES+II+IHP+IIU (2)
(ii) in case the cascade failure effect in a dam series is ascertained, the rating points sh all consider all the
affected dams in the system, regardless of the potential dams’ ownership conflicts or administrative
jurisdiction differences.
(iii) the following procedure shall be followed to estimate the rating points for each of the sub - categories : -
(I) Reservoir contents or water supply index(𝐈𝐑𝐄𝐒): The value of the reservoir contents shall be calculated as
a function of the time that it w ould take to fill the reservoir and t he time is computed in months, by dividing
the reservoir volume in million cubic metre ( Mm3) by the average river flow in m3/s (average of daily
means, not daily peaks), and converting the resulting number into months by multiplying it by 0. 386.
Example; - If there is a reservoir with volume of 1200 Mm3, and an average flow of 40 m3/s, the time to fill the reservoir
with the average river flow shall then be:
TF=VQ⁄∗0.386 (3)
Where,
TF = Time to fill the reservoir in months
V = Volume of the reservoir in Mm3
Q = Average river flow in m3/s 020406080100120
1 10 100Points (IDH)
Dam Height (m)
Applying the equation to the values in the example, we get
TF= 1200/40*0.386 = 11.5 months
The time to fill is entered into Figure 3 , and for the 11.4 months, shall be read as 23.7 points , and a n alternative way to
compute the number of points is by using the following formula ; namely; -
IRES{5024⁄∗TF ,(for TF<24)
100 ,(for TF≥24) (4)
Where,
IRES = Reservoir Content or water supply Index
Figure 3 - Consequences Rating Points for Reservoir Content Index (I RES)
(II) Irrigation land index(𝐈𝐈): Consequences rating points for irrigated land index shall be calculated as
specified in Figure 4 .
The number of points for irrigated land is also computed as:
II{area ,(for area <100)
100 ,(for area ≥100) (5)
Where,
𝒂𝒓𝒆𝒂 = irrigated area in 1,000 ha.
𝑰𝑰 = irrigated land index
(III) Hydropower generation index(𝐈𝐇𝐏): Consequences rating points for hydropower generation index shall
be calculated as specified in Figure 5.
The hydropower generation index can also be computed by:
IHP{P10⁄ ,(for P <1000)
100 ,(for P ≥1000) (6)
Where,
P = installed capacity in MW.
IHP = Hydropower index
Figure 4 - Consequences Rating Points for Irrigated Land Index (I I)
Figure 5 - Consequences Rating Points for Hydropower Generation Index (I HP)
(IV) Industrial use index (𝐈𝐈𝐔): The corresponding rating points shall be calculated using the same
methodology as explained for waters supply index and specified in Figure 3 and equation (3).
(b) Potential for loss of life . – (1) The potential for loss of life shall be estimated indirectly through the estimation
of the total population at risk in the downstream areas and this category shall consider the severity of the breach
or failure flood, and the approximate arrival time of the flood wave, which shall be an indi rect measure of the
available warning time.
(2) In this category, as in the project benefits index (I PB), the evaluation of failure consequences of a dam in a
cascade system shall include the failure consequences of dams located downstream if such failure be caused
by the dam under scrutiny and if that failure shall not otherwise have occurred in the scenario under study.
(3) The rating points sh all consider the consequences of all dams involved, regardless of the potential dams’
ownership conflicts or administrative jurisdiction differences.
(4) In cases where the failure of the downstream dam is ascertained, the highest hazard category m ay be
adopted without the need for further justifications.
A. Incremental population at risk index (IPAR). – (i) An envelope curve for estimating the potential loss of life
(PLL) when there is great er than five minutes of warning, but less than ninety minutes, may be expressed as a
function of the population at risk (PAR) as
PLL = PAR0.6 (7)
Equation ( 7) has been used to establish the general shape of the utility curve for the PAR ( Figure 6 ).
Equation (8) below can also be used for numerical calculation
IPAR{20∗PAR0.2954,(for PAR<100,000)
600 ,(for PAR ≥100,000) (8)
Where,
PAR = incremental population at risk
(ii) As the equation (8) specifie s, the incremental population at risk sh all be used in this approach by subtracting
from the consequences of the dam failure , the ones that would have happened by the natural flow anyway, that is,
even if the dam had not failed , provided , for a sunny -day failure scenario (normal operation), incr emental and total
consequences are to be considered equal.
Table 6 - Highest Severity Categories1 used to estimate Population at Ris
Hazard
Vulnerability
Classification1 Description Classification
Limit
(Depth *
Velocity) Limiting
Water Depth
(m) Limiting
Velocity
(m/s)
H3 Unsafe for children, elderly and
vehicles D*V <0.6 1.2 2.0
H4 Unsafe for vehicles and people. D*V < 1.0 2.0 2.0
H5 Unsafe for vehicles and people. All
buildings vulnerable to structural
damage. Some less robust buildings
subject to failure. D*V < 4.0 4.0 4.0
Table 6 - Highest Severity Categories1 used to estimate Population at Risk
H6 Unsafe for vehicles and people. All
building types considered
vulnerable to failure. D*V > 4.0 - -
Notes:
1Complete Categories are shown in Figure 1 and Table 2
Figure 6 - Consequences Rating Points for Incremental Population at Risk (I PAR)
(iii) The population at risk shall be estimated using the vulnerability approach specified in regulation 5. Only the
population exposed to the highest hydraulic conditions (classes H3 to H 6, Table 6), shall be considered as
at risk, and shall be counted in the index calculation and t o obtain a full advantage or benefit of the flood
severity analysis, the use of a two -dimensional depth -averaged (2DH) hydraulic model is recommended.
(iv) The adequacy of warning to the downstream population has not been considered for the index estimation of
this category.
(v) The population at risk estimation and index sh all reflect the current downstream development and the future
development plans, especially for dams in planning or under construction stage.
B. Critical arrival time index (IAT): The factors or conditions to be considered for critical arrival time index shall
include the following, namely: -
(i) the effectiveness of the warning and evacuation process ;
(ii) successful evacuation depend s on the time available until the arrival of the floodwater in an area and the
time required for evacuation and the following t wo elements determine the time available for evacuation:
(a) The time available between the first s igns and the initiation of the flood, i.e. the breach ; and
(b) The time available between the breach initiation and the arrival of the floodwaters at a certain location
(called arrival time).
(iii) the time lag between first signs and the in itiation of a flood depends on the (threatening) types of flood and
the availability of warning systems. The “critical” arrival time calculation is recommended , understanding
as “critical” the minimum wave arrival time computed in the nearest populated area downstream the dam
(i.e. town, city, village). This value can be easily obtained after the dam break analysis study is carried out ;
(iv) Researches by the U nited States Bureau of Reclamation (Graham, 1999) on the field of the potential loss of
life, found that with 90 minutes or more of warning time the toll of victims was considerably lower even in
cases where thousands had to be evacuated ;
(v) The utility curve for the arri val time index was developed (Figure 7) assigning the highest rating points
(100 points) to those cases with less than ninety minutes between the breach initiation process and the
moment the nearest population start to be inundated. After ninety minutes, the rating or penalty points are
exponentially reduced until a minimum of zero points, when a minimum of 12 hours of arrival time is
computed ;
(vi) If a numerical estimation of the critical arrival index is preferred, equation (9) below may be used
𝑰𝑨𝑻
{ 𝟏𝟎𝟎,(𝒇𝒐𝒓 𝑨𝑻≤𝟏.𝟓 𝐡𝐫𝐬)
𝟏𝟒𝟑.𝟐𝟖∗(𝟎.𝟕𝟖𝟔𝟖)𝑨𝑻,(𝒇𝒐𝒓 𝟏.𝟓<𝐴𝑇<48)
𝟎,(𝒇𝒐𝒓 𝑨𝑻≥𝟒𝟖 𝐡𝐫𝐬)(9)
Where, 𝑨𝑻 = critical arrival time in hours
𝑰𝑨𝑻 = critical arrival time index
Figure 7 - Consequences Rating Points for Critical Arrival Time Index (I AT)
(c) Potential for property damage . – (1) Property damage category shall include damage to inhabited dwellings,
commercial and industrial developments, agricultural lands and crops, roads, highways and utilities and the
associated economic losses both permanent and temporary and shall include damages to lifeline facilities and
economic disruption.
(2) The indexes specified in this category, are meant to identify the relative magnitude of losses against a broad
scale of values and n o attempt shall be made to assess actual market value or actual Indian rupees losses. A total
of ten sub-indexes were developed to estimate the potential damage to properties is specified in Table 7.
(3) The range of consequences rating points listed in Table 7 reflect both the importance of a facility and the
relative magnitude of expected dam ages based on the hydraulic conditions of the flood (severity). The final
value for each index shall be selected within the range depending upon the flood severity class obtained from the
inundation maps results and the total area affected. Table 7 specifi es the general guidance in the severity classes
to be considered in each case. If any item is located out of those classes, the final index should be considered as
zero.
(4) Utility curves serve as a guide in the calculation of rating points of each type of property. A larger or smaller
value may be selected depending on the need for conservatism in protecting the facility or area that could be
damaged. Practical illustration in how to use the utility curves is specified in Schedule A.
(5) The final property dama ge index is given by the sum of all the rating points as follows:
𝑰𝑷𝑫=𝑰𝑵𝑯+𝑰𝑺𝑯+𝑰𝑹+𝑰𝑰𝑪+𝑰𝑨𝑨+𝑰𝑹𝑨𝑹+𝑰𝑹𝑨𝑼+𝑰𝑾𝑺+𝑰𝑬𝑹+𝑰𝑬𝑷 (10)
Where,
𝑰𝑷𝑫 = Property Damage Index.
𝑰𝑵𝑯 = National Highways index
𝑰𝑺𝑯 = State Highways index
𝑰𝑹 = Railroads index
𝑰𝑰𝑪 = Industrial and Commercial use Index
𝑰𝑨𝑨 = Agricultural/Aquaculture use Index
𝑰𝑹𝑨𝑹 = Residential Areas (Rural) Index
𝑰𝑹𝑨𝑼 = Residential Areas (Urban) Index
𝑰𝑾𝑺 = Water Supply/Treatment Facilities index
𝑰𝑬𝑹 = Emergency Response Facilities index
𝑰𝑬𝑷 = Electric Power Facilities
Table 7 - Consequences Indexes for Potential Property Damage Category
(d) Potential for Environmental Damage
(1) This component of the hazard potential assessment takes into consideration the impact over the environment and
cultural heritage sites, specifically to those considered as protected areas in the country.
(2) Conservation or Protected Areas are defined as areas of notable environmental or historical interest or
importance which are protected by law against undesirable changes. These areas are conserved by varying levels
of legal protection which are given by the policies formulated by the government of India or global conve ntions.
Notes:
1 Rating points per area/length affected. If there is no item/facility affected within the
severity classes zero points should be used
2 Flood Severity Categories to be considered to estimate final rating points along with
relative importance of the item/fa cility and the extents of the impact
(3) The proposed indexes to evaluate the impact under this category are specified in Table 8. Potential Environment
and Cultural index (I ECI) can be calculated as follows:
𝑰𝑬𝑪𝑰=𝑰𝑷𝑨+𝑰𝑪𝑯 (11)
Where,
𝑰𝑬𝑪𝑰 = Environmental and Cultural Index.
𝑰𝑷𝑨 = Protected Areas Index
𝑰𝑪𝑯 = Cultural Heritage Index
Table 8- Consequences Indexes for Potential Environment and Cultural impact
Indicator
Parameter Type of Property Index Rating Points1 Flood Severity
Class2
Protected Areas National Parks, Wildlife
Sanctuary, Community
Reserve, Conservation Reserve IPA 5 - 50 H3 – H6
Cultural Heritage World and National heritage
sites (temples, monuments,
caves) ICH 5 - 50 H5 – H6
Notes:
1 Rating points per item/site affected. If there is no item/site affected within the severity classes, zero points should be
used
2 Severity Categories to be considered to estimate final rating points along with relative importance of the site
14. Dam Classification and the Potential Consequences Index (P CI). - (1) As part of the final step in the additive
weighting scheme specified in sub -regulation (3) of regulation 13 , the final hazard potential classification shall
be obtained after adding up all the index values (rating points) for each of the categories. For that purpose,
equation (12) may be used:
𝑷𝑪𝑰=𝑰𝑫𝑯+𝑰𝑷𝑩+𝑰𝑷𝑨𝑹+𝑰𝑨𝑻+𝑰𝑷𝑫+𝑰𝑬𝑪𝑰 (12)
Where,
𝑷𝑪𝑰 = Potential Consequences Index.
𝑰𝑫𝑯 = Dam Height index
𝑰𝑷𝑩 = Project Benefits index
𝑰𝑷𝑨𝑹 = Population at Risk Index
𝑰𝑨𝑻 = Critical Arrival time Index
𝑰𝑷𝑫 = Property Damage Index
𝑰𝑬𝑪𝑰 = Environmental and Cultural Index
(2) The final hazard potential class will be a function of the total rating points, i.e. the value of the Potential
Consequences Index ( PCI) and Table 4 describes the relationship of the consequence’s categories with the final
hazard class .
(3) Dams with total consequences index near the boundaries between two classes (+/ - 50 points) shall be
comprehensively assessed and additional engineering judgment shall be used to determine the actual hazard
classificatio n.
ANIL JAIN , Chairman
[ADVT. -III/4/Exty./ 766/2024 -25]
SCHEDULE A
Summary of Utility Curves for Points Score Estimation (Property Damage and Environmental/Cultural Impact)
Figure C. 1 - Utility Curves for Point Score Estimation of National Highways
Figure C. 2 - Utility Curves for Point Score Estimation of State Highways
Figure C. 3 - Utility Curves for Point Score Estimation of Railways
Figure C. 4 - Utility Curves for Point Score Estimation of Industrial & Commercial Land Use
Figure C. 5 - Utility Curves for Point Score Estimation of Agricultural Land Use
Figure C.6 - Utility Curves for Point Score Estimation of Built -up Urban Land Use
Figure C. 7 - Utility Curves for Point Score Estimation of Built -up Rural Land Use
Figure C. 8 - Utility Curves for Point Score Estimation of Water Supply/Treatment Facilities
Figure C. 9 -Utility Cu rves for Point Score Estimation of Emergency Response Facilities
Figure C. 10 - Utility Curves for Point Score Estimation of Electric Power Facilities
Figure C. 11 - Utility Curves for Point Score Estimation of Protected Areas
Figure C. 12 - Utility Curves for Point Score Estimation of Cultural Heritage Sites
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