International Journal of Forest, Animal and Fisheries Research (IJFAF)
ISSN: 2456-8791
[Vol-9, Issue-3, Jul-Sep, 2025]
Issue DOI: https://dx.doi.org/10.22161/ijfaf.9.3
Article DOI: https://dx.doi.org/10.22161/ijfaf.9.3.1
Int. J. Forest Animal Fish. Res.
www.aipublications.com/ijfaf Page | 1
Effects of Climatic Factors on Crocodilians in North
India
Anjali Garg, Dr. Navpreet Kaur*
Department of Zoology, Deshbhagat University, Gobindgarh, Punjab, India
*Corresponding Author
Received: 22 Jul 2025; Received in revised form: 19 Aug 2025; Accepted: 23 Aug 2025; Available online: 28 Aug 2025
©2025 The Author(s). Published by AI Publications. This is an open-access article under the CC BY license
(https://creativecommons.org/licenses/by/4.0/)
Abstract— Climatic variables — especially air temperature, precipitation patterns, and river flow regimes — are
critical drivers of crocodilian biology and demography. In North India, the two primary crocodilian taxa of
conservation concern are the mugger (Crocodylus palustris) and the gharial (Gavialis gangeticus). Climate-
driven changes influence nesting success, incubation temperatures (and therefore sex ratios via temperature-
dependent sex determination), habitat availability through altered river hydrology and flooding regimes, and
physiological stress. Here we synthesize recent literature and propose a research framework to quantify climate
impacts on crocodilians in North India. Key findings from the literature indicate that (1) incubation temperature
strongly influences sex determination in crocodilians, (2) altered river flows and flood regimes can both create and
destroy suitable nesting/foraging habitats, and (3) anthropogenic habitat disturbance combined with climatic
extremes increases physiological stress and mortality risk. We provide recommendations for monitoring, habitat
management, and modelling approaches to inform conservation planning under future climate scenarios.
Keywords— Crocodylus palustris, Gavialis gangeticus, climate change, temperature-dependent sex
determination, river hydrology, North India, conservation.
I. INTRODUCTION
Crocodilians are apex predators and ecosystem
engineers in riverine and wetland systems; they also
serve as indicators of aquatic ecosystem health. In
India, the mugger (C. palustris) and gharial (G.
gangeticus) occupy a range of riverine, lacustrine and
reservoir habitats in the Gangetic plains and
associated tributaries of North India. Climatic drivers
(temperature, precipitation, and extreme weather
events) strongly modulate the physical environment
used by crocodilians, and through that influence
reproductive biology, juvenile survival, foraging
ecology, and population dynamics. Notably, many
crocodilian species exhibit temperature-dependent
sex determination (TSD), making reproductive
output and future population sex ratios sensitive to
changes in incubation microclimate. Changes to river
flow regimes (timing, magnitude, frequency) caused
by altered precipitation, glacier melt, or
anthropogenic flow regulation also reshape nesting
beaches and prey availability. This review
synthesizes current knowledge on climate impacts on
crocodilians in North India and outlines a practical
framework to study and manage these effects.
II. OBJECTIVES AND RESEARCH
QUESTIONS
Primary objective: synthesize evidence and provide
an implementable research plan to quantify how
climatic factors affect crocodilian reproductive
success, population structure, and habitat suitability
in North India.
Specific research questions:
Garg and Kaur International Journal of Forest, Animal and Fisheries Research (IJFAF)
9(3)-2025
Int. J. Forest Animal Fish. Res.
www.aipublications.com/ijfaf Page | 2
1. How do ambient and nest temperatures during
incubation influence sex ratios and hatchling
fitness in C. palustris and G. gangeticus?
2. What are the impacts of altered hydrology (flood
frequency, dry-season flows) on nesting habitat
availability and juvenile survival?
3. Does exposure to climatic extremes (heatwaves,
prolonged droughts, extreme floods) increase
physiological stress and mortality?
4. How will projected climate scenarios alter habitat
suitability and population viability over the next
30–50 years?
III. BACKGROUND — KEY BIOLOGICAL
AND CLIMATIC MECHANISMS
3.1 Temperature-dependent sex determination
(TSD)
Crocodilians show TSD: incubation temperature
during a thermosensitive period determines
hatchling sex, often with narrow pivotal
temperatures producing balanced sex ratios. Small
directional shifts in incubation temperatures (caused
by ambient warming, changes in nest shading, or
altered wet–dry cycles) can produce skewed sex
ratios with long-term demographic consequences.
Empirical work on C. palustris demonstrates clear
incubation temperature ranges that produce
predominantly females at lower temperatures and
males at slightly higher temperatures (and complex
FMF patterns in some species). Therefore, increasing
mean and extreme temperatures during nesting
seasons may bias sex ratios.
3.2 River flow, nesting beaches and habitat
dynamics
Riparian and sandbar geomorphology determine
availability of suitable nesting sites. Climate-driven
changes in monsoon timing, intensity, or glacial melt
can alter sediment deposition and floodplain
dynamics. Both increased extreme floods and
prolonged low flows can reduce nest success —
floods may inundate nests and cause clutch loss,
while low flows can reduce prey base and
concentrate predators. Modelling studies for gharials
indicate shifting habitat suitability under climate
change, including loss of critical river stretches.
3.3 Physiological stress and population health
Field studies have documented elevated
physiological stress markers (e.g., glucocorticoid
metabolites) in muggers exposed to habitat
disturbance and likely compounded by climatic
stressors. Chronic stress can reduce immune function,
lower reproductive output and increase mortality,
particularly when climatic extremes are coupled with
anthropogenic pressures.
IV. SUGGESTED METHODS (FIELD AND
ANALYTICAL)
4.1 Study sites & design
Select 6–10 ponds across a latitudinal and
hydrological gradient in North India (include
Chambal, Yamuna tributaries, habitat near Crocodile
Breeding Centres).
Stratify by river regulation (free-flowing vs
regulated), anthropogenic disturbance, and nesting
presence.
4.2 Climatic and hydrological data
Obtain historical and near-real-time climatic data (air
temperature, precipitation) from IMD and local
weather stations. Use remote-sensing products for
land surface temperature where station data are
sparse.
River discharge, stage and sediment transport data
from Central Water Commission (CWC) and state
water agencies. For future projections, use CMIP6
downscaled climate projections under RCP/SSP
scenarios.
4.3 Nest monitoring & microclimate
Locate and monitor nests during the breeding season.
Install data loggers in a subset of nests to record nest
temperature and moisture at 30–60 minute intervals
through incubation. Measure nest exposure
(sun/shade), substrate type, vegetation cover, and
distance from waterline.
Record clutch size, hatch success, hatching date, and
sex of hatchlings (molecular or morphological sexing
methods recommended if sexual dimorphism is
absent until maturity).
4.4 Physiological stress metrics
Collect non-invasive samples (faeces, shed scutes) or
blood (when permitted) to measure stress hormone
Garg and Kaur International Journal of Forest, Animal and Fisheries Research (IJFAF)
9(3)-2025
Int. J. Forest Animal Fish. Res.
www.aipublications.com/ijfaf Page | 3
(corticosterone/cortisol metabolites), body condition
indices, and basic hematology.
4.5 Habitat & prey surveys
Quantify prey abundance (fish surveys,
netting/echosounder), bank substrate composition,
and nesting beach geomorphology annually. Map
nesting beaches using drone photogrammetry to
assess size and elevation relative to flow stage.
4.6 Analytical approach
Use generalized linear mixed models (GLMMs) to
relate hatch success and sex ratio to nest
microclimate and site variables; include random
effects for site/year.
Use species distribution models (MaxEnt, ensemble
SDMs) to project habitat suitability under current
and future climate scenarios.
Apply population viability analysis (PVA)
incorporating temperature-dependent sex ratios to
simulate long-term demographic consequences
under climate projections.
Use change-point detection to examine shifts in river
flow regimes and correlate with nesting success and
recruitment.
V. LITERATURE-BASED RESULTS
(SYNTHESIS)
(This section synthesizes findings from recent studies
rather than presenting new field data.)
⚫ TSD sensitivity: Laboratory and captive studies
demonstrate that C. palustris exhibits TSD with
narrow temperature windows producing
specific sexes; small temperature shifts may
change sex ratios significantly. Documented
pivotal temperatures and published
experimental temperature-sex curves exist for
crocodilians and muggers specifically.
⚫ Habitat vulnerability to altered flow regimes:
Modeling and empirical studies for gharials and
muggers show that river flow alterations (timing
and magnitude) reduce available nesting habitat
and fragment populations. Predicted climate
change impacts will likely reduce continuous
stretches of suitable river habitat for gharials
and may shift mugger distribution in response
to new reservoir/river conditions.
⚫ Physiological stress linked to disturbance and
extremes: Recent field work in Indian urban and
semi-urban systems recorded elevated stress
markers in muggers exposed to disturbance;
climatic extremes (heatwaves, drought) are
expected to exacerbate stress-related health
declines.
⚫ Conservation concern and management
implications: National and regional reports
highlight climate change as an emerging threat
to crocodilian conservation, with calls for
adaptive management (nest protection,
managed releases, habitat restoration, flow
regime conservation).
VI. DISCUSSION
The combined evidence indicates that climatic
variation interacts synergistically with anthropogenic
threats to shape crocodilian population trajectories in
North India. TSD implies that even modest warming
during nesting seasons could produce sex-biased
cohorts, potentially undermining effective
population replacement over decades. Hydrological
changes — whether from altered monsoon patterns,
increased flood frequency, or regulated discharge —
can rapidly change nesting beach morphology and
juvenile survival. Physiological stress resulting from
habitat degradation and climatic extremes reduces
resilience and likely increases mortality risk.
Conservation responses need to be anticipatory,
combining monitoring of nest microclimate and sex
ratios with habitat protection (river flow
management, sandbar/nesting beach preservation),
and ex-situ measures where necessary (e.g., managed
incubation to ensure balanced sex ratios). Integrating
long-term climate projections into species
distribution and PVA models will produce actionable
scenario planning for reserves and Project Crocodile
interventions.
VII. MANAGEMENT RECOMMENDATIONS
(PRACTICAL ACTIONS)
⚫ Nest microclimate monitoring network:
Establish standardized nest-monitoring across
major river systems during breeding seasons;
deploy temperature loggers in representative
nests to directly measure incubation conditions.
Garg and Kaur International Journal of Forest, Animal and Fisheries Research (IJFAF)
9(3)-2025
Int. J. Forest Animal Fish. Res.
www.aipublications.com/ijfaf Page | 4
⚫ Adaptive nest management: Where monitoring
shows dangerous sex biases or high nest
mortality (due to flooding/heat), implement
managed incubation protocols (shade structures,
artificial incubation at controlled temperatures,
or nest relocation) as short-term emergency
interventions.
⚫ River flow safeguards: Work with water
authorities to maintain environmental flows
during nesting and early juvenile seasons to
preserve nesting beaches and prey availability;
avoid sudden release regimes that inundate
nests.
⚫ Habitat restoration & protection: Protect key
sandbar and riverbank nesting habitats from
sand mining, riverbank development, and
excessive tourism; use river reach zoning to
reduce human disturbance during the
reproductive season.
⚫ Long-term modelling & monitoring: Implement
SDM + PVA pipelines to forecast habitat
changes and demography under SSP scenarios;
update management strategies iteratively as
data accrue.
⚫ Community-based conservation: Engage local
communities as nest guardians and citizen
scientists; incorporate local knowledge to time
protective measures and reduce conflict.
VIII. LIMITATIONS AND FUTURE
DIRECTIONS
⚫ Empirical data on temperature-sex responses for
wild C. palustris and G. gangeticus across North
Indian climatic gradients remain sparse;
targeted experimental and field studies are
needed.
⚫ Downscaling global climate model outputs to
river reach scale remains challenging;
hydrological modelling that couples climate,
glacier/snowmelt (in headwaters), and human
flow regulation is essential.
⚫ Socioeconomic drivers (e.g., irrigation demand,
dam operations, sand mining) frequently
interact with climate drivers and must be
included in integrated management frameworks.
IX. CONCLUSION
Climatic factors — primarily temperature and
hydrology — play central roles in shaping
crocodilian reproduction, habitat suitability, and
population dynamics in North India. The presence of
TSD, sensitivity of nesting sites to flow regimes, and
evidence of physiological stress make crocodilians
vulnerable to climate change, particularly when
combined with anthropogenic habitat alteration.
Implementing a combined program of nest
microclimate monitoring, adaptive nest management,
flow protection, and predictive modelling will
strengthen conservation outcomes for muggers and
gharials in the region.
REFERENCES
[1] Lang, J. W. (1994). Temperature-dependent sex
determination in crocodilians and other reptiles. Journal of
Experimental Zoology. [Review summarizing TSD in
crocodilians].
[2] Whitaker, R., & Whitaker, Z. (1984). Nesting behaviour
of mugger crocodiles and notes on clutch parameters.
[Classic field studies summarized in later syntheses].
[3] Monitoring the stress physiology of free-ranging
mugger crocodiles: recent field observations and
hormone analysis. (2024). PMCID article.
[4] Riverine Realities: Evaluating Climate Change Impacts
on Habitat Dynamics of the Critically Endangered
Gharial (Gavialis gangeticus) in the Indian Landscape.
(2024). Animals (MDPI).
[5] ZoosPrint. (year). Climate Change as a new challenge for
conservation of Crocodiles. (Discussion of climate-related
nest and flow impacts).
[6] Current State of Mugger Populations — review and
captive studies reporting incubation temperature
effects. (PMC article).
[7] India Mongabay article (2024): Mugger crocodiles may
be physiologically stressed in disturbed habitats. (field
evidence and conservation context).

Effects of Climatic Factors on Crocodilians in North India

  • 1.
    International Journal ofForest, Animal and Fisheries Research (IJFAF) ISSN: 2456-8791 [Vol-9, Issue-3, Jul-Sep, 2025] Issue DOI: https://dx.doi.org/10.22161/ijfaf.9.3 Article DOI: https://dx.doi.org/10.22161/ijfaf.9.3.1 Int. J. Forest Animal Fish. Res. www.aipublications.com/ijfaf Page | 1 Effects of Climatic Factors on Crocodilians in North India Anjali Garg, Dr. Navpreet Kaur* Department of Zoology, Deshbhagat University, Gobindgarh, Punjab, India *Corresponding Author Received: 22 Jul 2025; Received in revised form: 19 Aug 2025; Accepted: 23 Aug 2025; Available online: 28 Aug 2025 ©2025 The Author(s). Published by AI Publications. This is an open-access article under the CC BY license (https://creativecommons.org/licenses/by/4.0/) Abstract— Climatic variables — especially air temperature, precipitation patterns, and river flow regimes — are critical drivers of crocodilian biology and demography. In North India, the two primary crocodilian taxa of conservation concern are the mugger (Crocodylus palustris) and the gharial (Gavialis gangeticus). Climate- driven changes influence nesting success, incubation temperatures (and therefore sex ratios via temperature- dependent sex determination), habitat availability through altered river hydrology and flooding regimes, and physiological stress. Here we synthesize recent literature and propose a research framework to quantify climate impacts on crocodilians in North India. Key findings from the literature indicate that (1) incubation temperature strongly influences sex determination in crocodilians, (2) altered river flows and flood regimes can both create and destroy suitable nesting/foraging habitats, and (3) anthropogenic habitat disturbance combined with climatic extremes increases physiological stress and mortality risk. We provide recommendations for monitoring, habitat management, and modelling approaches to inform conservation planning under future climate scenarios. Keywords— Crocodylus palustris, Gavialis gangeticus, climate change, temperature-dependent sex determination, river hydrology, North India, conservation. I. INTRODUCTION Crocodilians are apex predators and ecosystem engineers in riverine and wetland systems; they also serve as indicators of aquatic ecosystem health. In India, the mugger (C. palustris) and gharial (G. gangeticus) occupy a range of riverine, lacustrine and reservoir habitats in the Gangetic plains and associated tributaries of North India. Climatic drivers (temperature, precipitation, and extreme weather events) strongly modulate the physical environment used by crocodilians, and through that influence reproductive biology, juvenile survival, foraging ecology, and population dynamics. Notably, many crocodilian species exhibit temperature-dependent sex determination (TSD), making reproductive output and future population sex ratios sensitive to changes in incubation microclimate. Changes to river flow regimes (timing, magnitude, frequency) caused by altered precipitation, glacier melt, or anthropogenic flow regulation also reshape nesting beaches and prey availability. This review synthesizes current knowledge on climate impacts on crocodilians in North India and outlines a practical framework to study and manage these effects. II. OBJECTIVES AND RESEARCH QUESTIONS Primary objective: synthesize evidence and provide an implementable research plan to quantify how climatic factors affect crocodilian reproductive success, population structure, and habitat suitability in North India. Specific research questions:
  • 2.
    Garg and KaurInternational Journal of Forest, Animal and Fisheries Research (IJFAF) 9(3)-2025 Int. J. Forest Animal Fish. Res. www.aipublications.com/ijfaf Page | 2 1. How do ambient and nest temperatures during incubation influence sex ratios and hatchling fitness in C. palustris and G. gangeticus? 2. What are the impacts of altered hydrology (flood frequency, dry-season flows) on nesting habitat availability and juvenile survival? 3. Does exposure to climatic extremes (heatwaves, prolonged droughts, extreme floods) increase physiological stress and mortality? 4. How will projected climate scenarios alter habitat suitability and population viability over the next 30–50 years? III. BACKGROUND — KEY BIOLOGICAL AND CLIMATIC MECHANISMS 3.1 Temperature-dependent sex determination (TSD) Crocodilians show TSD: incubation temperature during a thermosensitive period determines hatchling sex, often with narrow pivotal temperatures producing balanced sex ratios. Small directional shifts in incubation temperatures (caused by ambient warming, changes in nest shading, or altered wet–dry cycles) can produce skewed sex ratios with long-term demographic consequences. Empirical work on C. palustris demonstrates clear incubation temperature ranges that produce predominantly females at lower temperatures and males at slightly higher temperatures (and complex FMF patterns in some species). Therefore, increasing mean and extreme temperatures during nesting seasons may bias sex ratios. 3.2 River flow, nesting beaches and habitat dynamics Riparian and sandbar geomorphology determine availability of suitable nesting sites. Climate-driven changes in monsoon timing, intensity, or glacial melt can alter sediment deposition and floodplain dynamics. Both increased extreme floods and prolonged low flows can reduce nest success — floods may inundate nests and cause clutch loss, while low flows can reduce prey base and concentrate predators. Modelling studies for gharials indicate shifting habitat suitability under climate change, including loss of critical river stretches. 3.3 Physiological stress and population health Field studies have documented elevated physiological stress markers (e.g., glucocorticoid metabolites) in muggers exposed to habitat disturbance and likely compounded by climatic stressors. Chronic stress can reduce immune function, lower reproductive output and increase mortality, particularly when climatic extremes are coupled with anthropogenic pressures. IV. SUGGESTED METHODS (FIELD AND ANALYTICAL) 4.1 Study sites & design Select 6–10 ponds across a latitudinal and hydrological gradient in North India (include Chambal, Yamuna tributaries, habitat near Crocodile Breeding Centres). Stratify by river regulation (free-flowing vs regulated), anthropogenic disturbance, and nesting presence. 4.2 Climatic and hydrological data Obtain historical and near-real-time climatic data (air temperature, precipitation) from IMD and local weather stations. Use remote-sensing products for land surface temperature where station data are sparse. River discharge, stage and sediment transport data from Central Water Commission (CWC) and state water agencies. For future projections, use CMIP6 downscaled climate projections under RCP/SSP scenarios. 4.3 Nest monitoring & microclimate Locate and monitor nests during the breeding season. Install data loggers in a subset of nests to record nest temperature and moisture at 30–60 minute intervals through incubation. Measure nest exposure (sun/shade), substrate type, vegetation cover, and distance from waterline. Record clutch size, hatch success, hatching date, and sex of hatchlings (molecular or morphological sexing methods recommended if sexual dimorphism is absent until maturity). 4.4 Physiological stress metrics Collect non-invasive samples (faeces, shed scutes) or blood (when permitted) to measure stress hormone
  • 3.
    Garg and KaurInternational Journal of Forest, Animal and Fisheries Research (IJFAF) 9(3)-2025 Int. J. Forest Animal Fish. Res. www.aipublications.com/ijfaf Page | 3 (corticosterone/cortisol metabolites), body condition indices, and basic hematology. 4.5 Habitat & prey surveys Quantify prey abundance (fish surveys, netting/echosounder), bank substrate composition, and nesting beach geomorphology annually. Map nesting beaches using drone photogrammetry to assess size and elevation relative to flow stage. 4.6 Analytical approach Use generalized linear mixed models (GLMMs) to relate hatch success and sex ratio to nest microclimate and site variables; include random effects for site/year. Use species distribution models (MaxEnt, ensemble SDMs) to project habitat suitability under current and future climate scenarios. Apply population viability analysis (PVA) incorporating temperature-dependent sex ratios to simulate long-term demographic consequences under climate projections. Use change-point detection to examine shifts in river flow regimes and correlate with nesting success and recruitment. V. LITERATURE-BASED RESULTS (SYNTHESIS) (This section synthesizes findings from recent studies rather than presenting new field data.) ⚫ TSD sensitivity: Laboratory and captive studies demonstrate that C. palustris exhibits TSD with narrow temperature windows producing specific sexes; small temperature shifts may change sex ratios significantly. Documented pivotal temperatures and published experimental temperature-sex curves exist for crocodilians and muggers specifically. ⚫ Habitat vulnerability to altered flow regimes: Modeling and empirical studies for gharials and muggers show that river flow alterations (timing and magnitude) reduce available nesting habitat and fragment populations. Predicted climate change impacts will likely reduce continuous stretches of suitable river habitat for gharials and may shift mugger distribution in response to new reservoir/river conditions. ⚫ Physiological stress linked to disturbance and extremes: Recent field work in Indian urban and semi-urban systems recorded elevated stress markers in muggers exposed to disturbance; climatic extremes (heatwaves, drought) are expected to exacerbate stress-related health declines. ⚫ Conservation concern and management implications: National and regional reports highlight climate change as an emerging threat to crocodilian conservation, with calls for adaptive management (nest protection, managed releases, habitat restoration, flow regime conservation). VI. DISCUSSION The combined evidence indicates that climatic variation interacts synergistically with anthropogenic threats to shape crocodilian population trajectories in North India. TSD implies that even modest warming during nesting seasons could produce sex-biased cohorts, potentially undermining effective population replacement over decades. Hydrological changes — whether from altered monsoon patterns, increased flood frequency, or regulated discharge — can rapidly change nesting beach morphology and juvenile survival. Physiological stress resulting from habitat degradation and climatic extremes reduces resilience and likely increases mortality risk. Conservation responses need to be anticipatory, combining monitoring of nest microclimate and sex ratios with habitat protection (river flow management, sandbar/nesting beach preservation), and ex-situ measures where necessary (e.g., managed incubation to ensure balanced sex ratios). Integrating long-term climate projections into species distribution and PVA models will produce actionable scenario planning for reserves and Project Crocodile interventions. VII. MANAGEMENT RECOMMENDATIONS (PRACTICAL ACTIONS) ⚫ Nest microclimate monitoring network: Establish standardized nest-monitoring across major river systems during breeding seasons; deploy temperature loggers in representative nests to directly measure incubation conditions.
  • 4.
    Garg and KaurInternational Journal of Forest, Animal and Fisheries Research (IJFAF) 9(3)-2025 Int. J. Forest Animal Fish. Res. www.aipublications.com/ijfaf Page | 4 ⚫ Adaptive nest management: Where monitoring shows dangerous sex biases or high nest mortality (due to flooding/heat), implement managed incubation protocols (shade structures, artificial incubation at controlled temperatures, or nest relocation) as short-term emergency interventions. ⚫ River flow safeguards: Work with water authorities to maintain environmental flows during nesting and early juvenile seasons to preserve nesting beaches and prey availability; avoid sudden release regimes that inundate nests. ⚫ Habitat restoration & protection: Protect key sandbar and riverbank nesting habitats from sand mining, riverbank development, and excessive tourism; use river reach zoning to reduce human disturbance during the reproductive season. ⚫ Long-term modelling & monitoring: Implement SDM + PVA pipelines to forecast habitat changes and demography under SSP scenarios; update management strategies iteratively as data accrue. ⚫ Community-based conservation: Engage local communities as nest guardians and citizen scientists; incorporate local knowledge to time protective measures and reduce conflict. VIII. LIMITATIONS AND FUTURE DIRECTIONS ⚫ Empirical data on temperature-sex responses for wild C. palustris and G. gangeticus across North Indian climatic gradients remain sparse; targeted experimental and field studies are needed. ⚫ Downscaling global climate model outputs to river reach scale remains challenging; hydrological modelling that couples climate, glacier/snowmelt (in headwaters), and human flow regulation is essential. ⚫ Socioeconomic drivers (e.g., irrigation demand, dam operations, sand mining) frequently interact with climate drivers and must be included in integrated management frameworks. IX. CONCLUSION Climatic factors — primarily temperature and hydrology — play central roles in shaping crocodilian reproduction, habitat suitability, and population dynamics in North India. The presence of TSD, sensitivity of nesting sites to flow regimes, and evidence of physiological stress make crocodilians vulnerable to climate change, particularly when combined with anthropogenic habitat alteration. Implementing a combined program of nest microclimate monitoring, adaptive nest management, flow protection, and predictive modelling will strengthen conservation outcomes for muggers and gharials in the region. REFERENCES [1] Lang, J. W. (1994). Temperature-dependent sex determination in crocodilians and other reptiles. Journal of Experimental Zoology. [Review summarizing TSD in crocodilians]. [2] Whitaker, R., & Whitaker, Z. (1984). Nesting behaviour of mugger crocodiles and notes on clutch parameters. [Classic field studies summarized in later syntheses]. [3] Monitoring the stress physiology of free-ranging mugger crocodiles: recent field observations and hormone analysis. (2024). PMCID article. [4] Riverine Realities: Evaluating Climate Change Impacts on Habitat Dynamics of the Critically Endangered Gharial (Gavialis gangeticus) in the Indian Landscape. (2024). Animals (MDPI). [5] ZoosPrint. (year). Climate Change as a new challenge for conservation of Crocodiles. (Discussion of climate-related nest and flow impacts). [6] Current State of Mugger Populations — review and captive studies reporting incubation temperature effects. (PMC article). [7] India Mongabay article (2024): Mugger crocodiles may be physiologically stressed in disturbed habitats. (field evidence and conservation context).