el niño 1997–98 and the hydrometeorological variability of chapala, a shallow tropical lake in...
TRANSCRIPT
El Nino 1997–98 and the hydrometeorological variability of
Chapala, a shallow tropical lake in Mexico
Irina Tereshchenkoa,*, Anatoliy Filonova, Artemio Gallegosb, Cesar Monzona,Ranulfo Rodrıguezb
aDepartment of Physics , University of Guadalajara, Apdo. Postal 4-040, Guadalajara 44421, Jal., MexicobInstituto de Ciencias del Mar y Limnologia, UNAM, Mexico, Mexico
Received 18 July 2000; revised 7 December 2001; accepted 22 March 2002
Abstract
One hundred years chronological water level fluctuations for Chapala Lake, a shallow tropical lake in west Mexico, as well as
their relationships with air temperature fluctuations, precipitation and Lerma River discharge are examined in this study. It is
shown, that these relationships were strongly revealed in the last 1997–98 El Nino, which caused anomalous air temperature
and evaporation increase throughout Western Mexico territory and, as a consequence, 1 m downturn of the Chapala lake level
since January till June, 1998. To investigate 1997–1998 El Nino-Southern Oscillation phenomenon (ENSO 1997–98)
AVHRR-NOAA satellite image analysis of the Chapala Lake surface water temperature (LCST) was performed. These images
provide a temperature database for 1996–99 (38 months). Analysis of annual and seasonal LCST fluctuations was carried out
using monthly averages for this period. Time series analysis on the LCST data suggest that seasonal surface temperature
variations may be almost completely obscured by the annual harmonic. In 1998 the temperature pattern was altered due to the El
Nino 1997–98 episode. In winter the water surface temperature was on average almost 1 8C lower than the temperature values
registered in 1996. However, for the summer and autumn of 1998, such temperatures were 1.5 8? higher in comparison with the
reference year of 1996. q 2002 Elsevier Science B.V. All rights reserved.
Keywords: Chapala Lake; Surface water temperature; El Nino 1997–98
1. Introduction
Lake Chapala, the largest in Mexico and third
largest in Latin America, has an average length-width
of 75 £ 22 km and an average depth of only 6 m, with
a maximum of 11 m (Fig. 1). Among shallow lakes,
Lake Chapala is the largest in the world (Sandoval,
1994; 1996). It plays an important role in the economy
of the region. Approximately 14 million people live in
large and small settlements around, including import-
ant industrial and cultural sites. The lake provides for
a mild climate and establishes a land-lake breeze
circulation throughout its costal area. Atmospheric
humidity in this area is also moderate which together
with the pleasant landscape, makes the lake a great
tourist attraction.
The lake’s tributary and out-flow rivers are the
Lerma and Santiago, respectively. Both rivers and the
lake form a unique reservoir system covering an area
of approximately 47 000 km2. The annual rainfall is
750 mm, and evaporation from the lake surface ranges
0022-1694/02/$ - see front matter q 2002 Elsevier Science B.V. All rights reserved.
PII: S0 02 2 -1 69 4 (0 2) 00 0 66 -5
Journal of Hydrology 264 (2002) 133–146
www.elsevier.com/locate/jhydrol
* Corresponding author.
E-mail address: [email protected] (I. Tereshchenko).
from 1000 to 1400 mm per year, resulting in a
negative balance. The deficit is offset by inflow from
the Lerma river (Mosino and Garcıa, 1973; Jauregui,
1995; Filonov and Tereshchenko, 1997, Filonov et al.,
1998). In dry years annual rainfall can drop to
500 mm and the lake does not contribute any water
to the Santiago river (Riehl, 1979). However, in the
high-rainfall years the annual precipitation can reach
1000 mm and an important volume of water exits
through this same river.
According to data from the national water
commission (Comision Nacional del Agua, Mexico;
CNA), approximately 1.28 £ 106 m3 of suspended
particles enter the lake via its tributary from the lake’s
watershed. The size of the particles can reach up to
0.5 mm and are mainly deposited in the eastern part of
the lake. The result is a decreasing depth by the
accumulation of particles in the bottom of the lake.
Suspended particles modify the water transparency.
Secchi disk depth measures 0.2 m close to the Lerma
entrance, whereas at the eastern end a value of 0.5 m
(Sandoval, 1994) has been recorded.
Suspended particles of anthropogenic origin heav-
ily contaminate the water entering the lake via the
Lerma River. Large investments in water treatment
are needed in order to clean this water for human
consumption. In addition, large quantities of nutrients
reach the lake in the form of water weeds such as lilies
(Eichchornia crassipes ) and tule species (Tupha
latifolia, T. dominguensis, T. angustifolia ), and
build up huge floating islands (Filonov et al., 1998).
The lake water level has dropped dramatically
during this century (Fig. 2a). According to the
Comision Nacional del Agua, Mexico from 1945 to
1955 the drop was nearly 4 m. Lake water level
records for several years indicate that the mean value
has remained about 96.4 m (CNA determines the lake
water level relative to a fixed reference mark of 87 m).
Fig. 1. (a) Batimetrical map of Chapala Lake. Depth is given in meters in relation to the 87 m depthmark. (b) Diagram showing superficial
temperature sections obtained from the AVHRR images. The dot represents the SBE-19 location. The instrument measured superficial
temperature fluctuation on October 18–19, 1996.
I. Tereshchenko et al. / Journal of Hydrology 264 (2002) 133–146134
After the 1955 drop, 2 years later the water level rose
5 m and kept a mean value of 97.1 for almost 20 years.
However, since 1977 the level started to drop again
and nowadays the level is only 1 m above the 1955
historical low of 91.9 m (Filonov, 1998).
Sandoval (1994) mentions that the lake has reached
its current status due to water usage of the Lerma for
irrigation and industrial needs, and to cover the
domestic demand of Guadalajara city. Also, some
water is withdrawn upland from the Lerma River and
some is pumped out of the lake to cover the needs of
the local villages. In sum, these volumes of water
exceed the target limit for water preservation. There-
fore, Sandoval (1994) states that the lake will dry out
by the year 2007.
However, the principal loss of water from the lake
is through evaporation. During the spring months,
from March to May, evaporation brings down the lake
water level, on average, 10 mm a day. The shallow
depths (1–2 m) and low transparency of water in the
east part of the lake create less thermal inertia and
allow for stronger heating in comparison with deeper
and more transparent portions of the lake, resulting in
higher evaporation rates (Filatov, 1983). In this
connection, Sandoval (1994) has proposed the con-
struction of a dam to cut off the eastern 20% of the
lake to lower these losses. Detailed measurements
have shown (Filonov and Tereshchenko, 1997) that
the shallow east sector has a surface water tempera-
ture of as much as 3 8C above that in the central area of
the lake. However, on the basis of these measurements
it is difficult to advance any conclusion about the east
sector as being the main evaporation area of the lake.
Resolution of this controversy would require a surface
water temperature monitoring program (weekly
measurements) of a year duration, at least.
Not all authors agree that the lake will dry up in the
next years. Filonov (1998) puts forward different
arguments based on numerical modeling. He states
that the main cause of the long period level
fluctuations is unfavorable climatic factors and not
just anthropogenic influence. But he fails to defini-
tively establish the causes of Chapala Lake water
level fluctuations, as well as of rainfall fluctuations
over its watershed.
Filonov (1998) also shows that the
Fig. 2. (?) Average fluctuations of the lake Chapala level monthly mean (1), air temperature in Guadalajara (2), precipitation on the Mexican
territory (3) and the mean annual Lerma River discharge (4). (b) Frequency spectrums of lake level fluctuations, temperature, precipitation and
the Lerma River discharge. Here 4a is the traditional spectrum estimation, and 4b is an estimation from the method of the maximum likelihood.
The vertical line indicates the 80 % confidence limit.
I. Tereshchenko et al. / Journal of Hydrology 264 (2002) 133–146 135
hydrometeorological regimen of Chapala Lake is
influenced by El Nino episodes. The El Nino 1997–98
event was the strongest of this century (Magana et al.,
1999; Strub and James, 2002). This event registered
unusually high air temperatures and consequently a
very intense dry season in the west-central Mexico. In
Guadalajara, Jalisco the monthly average air tem-
perature from March to May 1998 was 3–4 8C higher
than the climatological mean for this same season.
The atmospheric relative afternoon humidity
decreased 6–8% (Tereshchenko and Filonov, 1998).
Due to the intense dry season, the lake lost more than
1 m of its water level due to evaporation and the
excess of water pumped to satisfy water demand from
the local industry and population (Filonov, 1998).
Measurements for water quality assessment and for
pollution dispersion in the Chapala Lake are con-
ducted irregularly and only at several discrete points.
But its thermodynamic condition is not monitored at
all. This complicates the development of scientific
concepts for the Chapala Lake rescue. The accessible
modern way of periodic monitoring of the lake’s
thermal mode can be achieved through the analysis of
surface water temperature satellite images, received
from the Advanced Very High Resolution Radio-
meters (AVHRR). Such analyses have found wide
application in physical oceanography (Scambos et al.,
1997; Soto-Mardones et al., 1999).
This work investigated long period fluctuations, as
well as seasonal variations in the lake’s hydrometeor-
ological regime and their relationship with the El
Nino 1997–98 event. In this analysis we have used
the monthly averages of AVHRR-NOAA satellite
images that were registered for more than three years.
2. Data and methods
2.1. Data
For the analysis of seasonal and interannual
variability of the hydrometeorological characteristics
of the lake and its surrounding area, we used the
following synchronous time series:
1. The 1900 to 1999 monthly average air temperature
series from the Guadalajara station located 50 km
from the lake.
2. The Lake Chapala level: (a) annual mean values
from 1900 to 1931, and (b) monthly means from
1932 to 1999.
3. The total precipitation in the Mexican territory
from 1941 to 1999.
4. For 1996 to 1999, the following series were used:
(a) the lake monthly average evaporation and lake
level, (b) the monthly average precipitation from
Chapala station, and (c) the Lerma River discharge.
Data were obtained from the Comision Nacional del
Agua, Mexico. In addition, Chapala Lake surface
temperature (CLST) data was received from the
AVHRR carried aboard the NOAA-12 and NOAA-14
polar orbiting satellites. These satellites operate in near
polar sun-synchronous orbits at a distance of about
850 km from the center of the Earth and provide global
coverage of the earth surface roughly twice a day. The
AVHRR has a 1.1 km2 resolution at nadir and is a five
channel device, measuring the Earth’s surface radiation
at visible, near infrared, and infrared wavelengths
(Monaldo, 1996; Schmugge et al., 1997; Barbosa,
1999). The CLST database was obtained from daily
images. This was done for the following local mean time
(LMT): 2:30, 6:30, 15:00 and 19:00 h (GTM þ 6 h).
The registered images of the 38 month period that
covered the Chapala Lake area (i.e. from April 1996
to May 1999) were used to prepare monthly CLST
composites (more than 4500 images). In the present
study four linear sections of the CLST were analyzed
(Fig. 1b): One with a west–east direction (section I)
and the remaining three running perpendicular to it,
with north–south direction (sections II, III and IV).
The initial daily CLST data at each section
represent a random sample of N data. On the time
coordinate there were N ¼ 4624 values, and from
1320 up to 8280 on the spatial one, depending on the
length of the section. Statistical analysis was applied
after data validation and their mean values, mean
square deviation and the 95% confidence limits over
space and time were computed. These were then used
to calculate more specific average values �T and root
mean square deviations sT (Walpole and Myers,
1993). The 95% confidence limits of the average daily
values of CLST were calculated with �T 2 d , �T0 ,�T þ d; where d ¼ t0:05sT=
ffiffiffiN
pis the 95% confidence
level and t0.05 is the deviation of the average of the
partial set �T with respect to the average of the general
I. Tereshchenko et al. / Journal of Hydrology 264 (2002) 133–146136
normal set �T0; determinated as: t0:05 ¼ ð �T 2�T0Þ=ðR=
ffiffiffiN
pÞ: Here R is the unbiased estimate of the
dispersion sT2; calculated as:
R ¼1
N 2 1
XNi¼1
ðTi 2 T0Þ
!1=2
:
2.2. Energy spectrum analysis
The estimation of the energy spectrum for each of
the time series was obtained by smoothing the
periodogram (Jenkins and Watts, 1969; Bendat and
Piersol, 1967, 1986; Konyaev, 1990):
SxxðvÞ ¼ð1
21Sxxðv
0ÞZðv2 v0Þdv0: ð1Þ
where Z(v ) is a smoothing function, and Sxx(v ) is
defined as the auto-periodogram:
SxxðvÞ ¼1
TCxðvÞCx
pðvÞ; ð2Þ
where Cx(v ) is the amplitude spectrum:
CxðvÞ ¼ðT
0xðtÞ expð2i2pvtÞdt
of the time series x(t ); T is the total length of the
series; (p) denotes the complex conjugate of the
amplitude spectrum. The standard algorithms
described in the literature (Jenkins and Watts, 1969;
Bendat and Piersol, 1967, 1986; Konyaev, 1990) were
used to calculate the confidence intervals for all
spectral estimates. The number of degrees of freedom
n, was found as n ¼ 2ð2F þ 1Þ; where F is the half-
width of the filter that is used to smooth the
periodograms. The mean square amplitudes of the
harmonics of the dominant peaks in the spectra were
found from the values of the spectral density.
The mean annual data of the Lerma River
discharge was used to find the energy peaks of the
spectra, by nonlinear methods of maximum like-
lihood, together with the traditional method of
spectral analysis (Burg, 1967, 1972; Akaike, 1969;
Konyaev, 1990). The spectral estimates from the
maximum likelihood method were calculated with
SðvÞ ¼ Dt=lAMLðvÞl2; ð3Þ
where the averaging filter was found by
AMLðvÞ ¼XNk; j
ak; j expð2i2pvðk 2 jÞDtÞ; ð4Þ
and the coefficients ak,j were obtained from the
inverse of the initial correlation matrix of the time
series:
Bð0Þ Bð1Þ · · · BðN 2 1Þ
Bð1Þ Bð0Þ · · · BðN 2 2Þ
· · · · · · · · · · · ·
BðN 2 1Þ BðN 2 2Þ · · · Bð0Þ
26666664
37777775
21
¼
a11 a12 · · · a1N
a21 a22 · · · a2N
· · · · · · · · · · · ·
aN1 aN2 · · · aNN
26666664
37777775 ð5Þ
Here M # N; M is the order of the white filter; N the
number of data points in the time series; and B(0),
Bð1Þ;…;BðM 2 1Þ are the data of the correlation
function of the time series analyzed.
2.3. Harmonic modelling
The seasonal fluctuations of the analyzed hydro-
meteorological characteristics, for example, tempera-
ture, represent the sum of annual and semi-annual
harmonics:
TðtÞ ¼ T0 þ A1 cos½2pðv1t þ w1Þ�
þ A2 cos½2pðv2t þ w2Þ� þ gðtÞ; ð6Þ
where T0 is the mean multi-annual air temperature in
the lake region; A1, A2, v1, v2, w1, w2 are the
amplitudes, frequencies, and initial phases of the
annual and semi-annual harmonic; g(t ) is the low and
high-frequency random component. All unknown
parameters in these equations were estimated by
discrete Fourier transformation using the initial time
series (Jenkins and Watts, 1969; Bendat and Piersol,
1967, 1986):
an ¼1
N
XNi¼1
Ti cosð2pn Dt=NÞ; ð7Þ
I. Tereshchenko et al. / Journal of Hydrology 264 (2002) 133–146 137
bn ¼1
N
XNi¼1
Ti sinð2pn Dt=NÞ; ð8Þ
and further were defined
T0 ¼1
N
XNi¼1
Ti; An ¼
ffiffiffiffiffiffiffiffiffiffiffiffian
2 þ bn2
q;
wn ¼ arctgðbn=anÞ:
ð9Þ
n ¼ 1; 2 are the annual and semi-annual harmonic; N
is the time series length ðN ¼ T=DtÞ; and Dt is the
time interval. Mean square deviations of the model
from the initial time series were calculated by the next
equation:
s ¼1
N 2 1
XNi¼1
ðTi 2 TmiÞ
!1=2
: ð10Þ
3. Results and discussion
3.1. Interannual and seasonal variability
Interannual and seasonal variability of the princi-
pal meteorological variables will allow us to under-
stand climatic features of the study area. Fig. 2a shows
monthly means of Chapala Lake water level fluctu-
ations, air temperature in Guadalajara, precipitation
over the Mexican territory and the mean annual
Lerma river discharge. Fig. 2b shows the spectra of
the analyzed time series.
The analysis of the diagrams reveals clear
relationship between long time fluctuations of the
lake water level and the Lerma River discharge. The
periods of the level downturn were always preceded
by years of low Lerma River discharge and, on the
contrary, several years of steadily high discharge of
the river resulted in increase of the lake level. The
relationship between the level and both long-period-
ical temperature fluctuations and river discharge is not
so obvious and it is difficult to find it with the visual
analysis alone. However, the results of applying
traditional and maximum likelihood spectral analysis
methods to the time series have confirmed the
presence of the fluctuations with the periods typical
for El Nino, i.e. from 2 to 7 years. The earlier
researches (Florescano and Swan, 1995; Magana et al.,
1999) have shown, that winters are more cold, and
both springs and summer beginnings are more hot and
arid in the Mexico territory during El Nino time. With
El Nino arrival the rain season begins one month later
and the precipitation intensity increases.
The seasonal variability of the meteorological
characteristics in the lake’s region is completely
determined by two overlapping harmonics (i.e. annual
and semi-annual), as well as by the contribution of
low-frequency components and the high frequency
random noise. Contribution of seasonal and sub-
seasonal harmonics (with periods of 4, 3 months, etc.)
is almost two orders of magnitude smaller than the
main harmonic, though such oscillations are clearly
separated in all the spectra (Mosino and Garcıa, 1973;
Filonov et al., 1998).
Results of the seasonal variability model are
presented in Table 1, the amplitude of annual
harmonics was on average five orders of magnitude
greater than the semi-annual amplitude for the same
time series. The maximum amplitude of the annual
harmonic occurred in mid May, and the maximum
amplitude of precipitation in early June. Concerning
the seasonal fluctuations of the lake water level, only
Table 1
Characteristics of annual and semi-annual harmonics of temporary series, given in Fig. 2(a). The amplitudes of harmonics and their
corresponding average square deviations are given. Their dimensions correspond to initial sizes. Initial phases are given in months
Data Annual harmonic Semi-annual har-
monic
s
Start date Stop date A1 w1 A2 w2
Air temperature (8C) 1/1/1900 8/1/1999 4.4 5.4 0.9 5.6 1.12
Precipitation (mm) 1/1/1941 8/1/1999 53.2 7.2 10.1 7.7 15.3
Lake level (m) 1/1/1900 8/1/1999 0.41 10.3 – – 1.75
I. Tereshchenko et al. / Journal of Hydrology 264 (2002) 133–146138
annual harmonics were seen with an amplitude about
40 cm with the maximum occurring in early October.
Fluctuations of the hydrometeorological parameters,
which are illustrated in Fig. 2a fitted satisfactorily to
the model, although the mean square deviations
between calculated values and the initial time series
are large.
3.2. Spatial–temporary variations in suface water
temperature
The CLST monthly mean values registered for
sections I, II, III and IV (Fig. 1b) were analyzed. They
are shown in Figs. 3–6. The letter a in these figures
represents a two-dimensional diagram where CLST is
a function of the spatial and temporary coordinates:
T(x,t ). The letter b refers to the average of all
analyzed time of measurements (38 months) of
temperature values on sections Tt(x ) and, finally, c
illustrates the time variation of the monthly average
temperature on sections Tx(t ).
The statistical characteristics of Tt(x ) and Tx(t ) for
all four sections calculated with algorithms described
in Section 2.1 are given in Table 2. It is clear that the
temperature averages over space and time for different
sections vary little. The changes of their mean square
amplitudes over space do not exceed 1 8C, but over
time they vary from 2.43 8C along section IV, up to
2.86 8C; along section I, and characterize the
amplitude of the CLST seasonal fluctuations.
The analysis of section I CLST (Fig. 3) suggests
that the water surface temperature in the central part
of the lake was on average 0.7 8C ðT ¼ 22:6 8CÞ
higher than in the western and the shallow eastern part
ðT ¼ 21:9 8CÞ: Such differences can be explained in
terms of the lake’s surface water circulation. During
the winter, water from the western and eastern parts of
the lake are strongly cooled and fully mixed with
shallow waters. However, in the central part where the
Fig. 3. Superficial temperature variability on section I. (a) The spatial–temporary diagram Tðx; tÞ: (b) Average spatial variability TtðxÞ; the
average was worked out from every pixel of temporary readout of all time period. (c) Average temporary variability of TxðtÞ; for all pixels of
section.
I. Tereshchenko et al. / Journal of Hydrology 264 (2002) 133–146 139
lake depth ranges from 6–10 m, the water surface
temperature was usually higher than in the western
and eastern parts.
Monthly means of the CLST time variation
(sections I–IV) fit closely to a ‘sine wave’ configur-
ation. It suggests the annual harmonic as the chief
contributor for the CLST seasonal fluctuations. The
contributions of the semi-annual and the high-
frequency harmonics are insignificant. CLST monthly
average fluctuations in 1996 and in the first half of
1997 had a ‘normal’ form (a ‘normal’ form means null
influence of El Nino on the CLST evolution).
However, modulation of the CLST time variation
became evident in November 1997. In 1998, the
surface temperatures were 0.2 8C (18.9 8C) lower in
January and 0.6 8C higher (25.4 8C) in August than
those for the corresponding months in 1996. Our
conjecture is that El Nino 1997–98 caused such
disturbance in the CLST evolution. On average in
winter 1997, all lake CLST were 0.9 8C lower than in
1996. In autumn 1998 such differences were even
more compared with 1996, thus reaching 1.4 8C.
The analysis of the spatial and temporal variability
of the CLST (sections II to IV, Figs. 3 and 4) indicates
that the northern part of the lake is about 1 8C higher
than the shallow eastern part. In the central part of the
lake, and in particular along section III, the CLST is
higher than along sections II and IV. A similar pattern
is seen along section I (Fig. 1). The period 1996–99
registered the lowest CLST, for example in winter
Fig. 4. Superficial temperature variability on section II. Figure explanation is similar to explanatory notes in Fig. 3.
Fig. 5. Superficial temperature variability on section III. Figure explanation is similar to explanatory notes in Fig. 3.
I. Tereshchenko et al. / Journal of Hydrology 264 (2002) 133–146140
1997–98. The highest CLST was registered in
summer 1998.
The average CLST course was modeled by
algorithms (1)–(5). The results are shown in
Table 2 and in Fig. 7. The sum of the annual
and semi-annual harmonics fitted well to the real
evolution of surface water temperatures for the
first 18 months. However, for the second 18
months, the CLST evolution deviated from
normal due to El Nino 1997–98 influence. In
this way the maximum negative deviations were
recorded in winter 1997–98 (20.9 8C) and the
positive deviations were registered in winter
1998–99 (post El Nino). They reached þ1.5 8C
in December 1998.
3.3. Influence of El Nino 1997–98 on daily CLST
We obtained CLST data four times daily. The
average values for sections I to IV were obtained
(Table 3). Daily CLST variation in 1996 and the first
half of 1997 did not exceed 2 8C (Fig. 8a). In the
winter of 1997–98, it increased up to 3 8C, and in
summer of 1998 it reached a value of 3.3 8C. In the
winter periods of 1996 – 97 and 1997 – 98, the
maximum daytime temperatures of the surface water
were up to 21 8C. However, the morning temperatures
in the cold winter of 1997–98 were 1.2 8C lower than
those of the previous year. In the summer of 1997 and
1998, the morning temperatures were the same, but
during the daytime they were higher than in previous
Fig. 6. Superficial temperature variability on section IV. Figure explanation is similar to explanatory notes in Fig. 3.
Table 2
The statistical characteristics of the LCST on the sections I–IV
Section number Averaging method Data quantity Average temperature
(8C)
Mean square amplitude
(8C)
95% Confidence limits
(8C)
I Space averaging 4624 21.67 2.86 ^0.071
Time averaging 8280 22.30 0.41 ^0.008
II Space averaging 4624 21.96 2.70 ^0.067
Time averaging 1320 22.32 0.37 ^0.103
III Space averaging 4624 21.94 2.87 ^0.071
Time averaging 1920 22.43 0.89 ^0.034
IV Space averaging 4624 21.75 2.43 ^0.060
Time averaging 2040 22.07 1.01 ^0.037
I. Tereshchenko et al. / Journal of Hydrology 264 (2002) 133–146 141
years. In Fig. 8a, the increase of the daily evolution of
the average CLST amplitude in the period July–
October 1998 is evident.
A special experiment was conducted to assess
the CLST daily evolution obtained by the AVHRR
images. The expriment consisted in establishing a
floating buoy at the intersection of sections I and
IV. Here, a SBE-19 with a temperature sensor was
attached to the buoy; leaving the sensor 5 cm
below the water surface. The instrument took
continuous readings throughout 2 days in October
1996, at time intervals of 10 s. The curve from
this experiment is shown in Fig. 8b. The CLST
registration times were 2:30, 6:30, 15:00 and
19:00 LMT. Bold points represent the congruence
of satellite data with the curve of the SBE-19
sensor. CLST data coincide well with the exper-
imental surface water temperatures.
The high-frequency fluctuations, shown in Fig.
8b occurred in the time period of 10–15 h. Such
fluctuations were caused by the influence of
breeze circulation on the temperature field. The
breeze over Chapala Lake is usually well
expressed and causes spatial and temporal varia-
bility in the distribution of the surface water
temperature. This was observed in various parts of
the lake (Filonov and Tereshchenko, 1999).
3.4. El Nino 1997–98 and fluctuations of
hydrometeorological characteristics
The evolution of the CLST was compared with the
variability of air temperature (from the Chapala
climatic station) and the surface water temperature
anomalies in the Pacific Ocean (Fig. 9). The
temperature anomalies were taken form the Monthly
Ocean Report (1996–99), for square B (48N–48S,
908W–1508W). The maximum phase of the El Nino
1997–98 took place in December, 1997 (Fig. 9c). One
month later, in January 1998, maximum temperature
increase occurred at active ocean layer and for the sea
level rise along the Mexican coast near the 208N
(Filonov and Tereshchenko, 2000; Strub and James,
2002). The maximum air temperature at the Chapala
climate station was recorded in June 1998 (Fig. 9b).
The peak of positive temperature anomalies in the
CLST time series was seen until December 1998.
(Fig. 9a).
The influence of El Nino 1997–98 was noticed
in the lake one year after its onset. El Nino
disturbed the typical course of the large-scale
circulation and the meteorological processes
within the Mexican territory; particularly in the
western part of the country. Here, the autumn and
winter of 1997–98 were extremely cold due to the
Fig. 7. Average temporary course from all four sections of Lake Chapala superficial temperature (curve 1) and its approximation by the sum of
annual and semi-annual harmonics (curve 2).
Table 3
Characteristics of annual and semi-annual harmonics obtained from the average data of the LCST four sections
Data Annual harmonic Semi-annual harmonic s
Start date Stop date A1 w1 A2 w2
LCST-1 4/1/1996 10/31/1997 2.91 7.4 0.58 7.8 0.08
LCST-2 11/1/1997 5/31/1999 – – – – 0.47
I. Tereshchenko et al. / Journal of Hydrology 264 (2002) 133–146142
Fig. 8. The course of superficial temperature in Lake Chapala. (a) Average superficial temperature of all four sections at 2:30 (curve 1), 6:30
(curve 2), 15:00 (curve 3) and 19:00 (curve 4) local mean time. (b) Superficial temperature recorded by the SBE-19 on October 18–19, 1996.
Dots represent AVHRR superficial temperature measurements occurring at the same time of the SBE-19 records.
Fig. 9. (a) Fluctuation difference of average temperature between curves 1 and 2, and its approximation. (b) The course of monthly average air
temperature at Chapala station. (c) The courses of monthly average anomalies of water superficial temperature in the Pacific Ocean (square B
(48N–48S; 908W–1508W)). (d) The course of monthly average precipitation (curve 1) and evaporation (curve 2) at Chapala station and the
Lerma River discharge (3). (e) The course of monthly average lake level.
I. Tereshchenko et al. / Journal of Hydrology 264 (2002) 133–146 143
advection of cold air from the north. In December
1997 the morning air temperature in the area of
Chapala Lake dropped 3 8C, with an occasional
snowfall (Informe Meteorologico Nacional, 1997–
98). Such low temperatures had not been regis-
tered for more than 100-years in the historical
record of the Instituto de Astronomıa y Meteor-
ologia (IAM, University of Guadalajara).
Conversely, the spring of 1998 in west-central
Mexico was extraordinarily hot. In June, the Chapala
climatic station recorded mean air temperatures of
28.2 8C. This was 5.4 8C higher than those registered
in June of the previous year. Such a dramatic rise in
air temperature caused a severe drought and multiple
forest fires. The latter were larger in number and
covered the entire country with a thick layer of smoke
that extended into the United States (Trasvina et al.,
1999; Filonov and Tereshchenko, 2000).
Fig. 9d and e give the temporal course of monthly
mean precipitation, evaporation (measured at climatic
station Chapala), Lerma River discharge and lake
Chapala level. They show that the high air tempera-
tures occurring in spring of 1998 caused an increase in
evaporation, and resulted in a sharp downturn of lake
level. In fact, the level decreased 1 m from January to
June 1998 (92.5 m), thus exceeding 0.6 m the minimal
1955 mark (91.9 m) in the historical hydrometric
record of the lake.
It is known that during El Nino events, the
precipitation regime in Northern America varies
strongly (Angel and Korshover, 1987; Philander,
1990). Hongbing and Furbish (1997) analyzed
long time series of precipitation (44 years) at
many points in the Florida Peninsula. Their
statistical analysis proved that El Nino and La
Nina are responsible for up to 40% variation in
annual precipitation, and up to 30% variation of
river discharges in Florida.
In the El Nino 1997–98, the mode of atmospheric
precipitation in Mexico changed drastically (Magana
et al., 1999). The seasonal rains in 1998 began at the
end of June (i.e. one month after its usual onset), and
precipitation was more intense than in the previous
(non El Nino) years. The plentiful precipitation in the
lake’s watershed increased the Lerma River dis-
charge. Thus the volume of water feeding the lake
increased the level by almost 1.5 m in November.
4. Summary and conclusion
The variability of the meteorological character-
istics in the Chapala Lake region is completely
determined by annual and semi-annual harmonics,
as well as by the contribution of lower (interannual
and decadal) frequency components. The contribution
of higher frequency harmonics (seasonal and sub-
seasonal) is almost two orders of magnitude smaller.
The amplitude of annual harmonics was on average
five orders of magnitude greater than the semi-annual
amplitude for the same time series. The analysis
shows that interannual fluctuations of Chapala Lake
water level are caused by changes in the cycles of
atmospheric circulation that occur in the lake’s
watershed area. The analysis of the diagrams reveals
clear relationship between long time fluctuations of
the lake water level and the Lerma River discharge.
The periods of the level downturn were always
preceded by years of low Lerma River discharge
and, on the contrary, several years of steadily high
discharge of the river resulted in increase of the lake
level. The results of applying traditional and maxi-
mum likelihood spectral analysis methods to the time
series have confirmed the presence of the fluctuations
with the periods typical for El Nino, i.e. from 2 to 7
years.
Our results also show that the lake’s thermodyn-
amics and its level are firstly determined by annual
variations, and secondly by lower frequency vari-
ations such as El Nino events and solar activity.
Analysis of the lake’s surface temperature obtained
from the AVHRR-NOAA images were on average
1 8C warmer in the north than in the south. The eastern
and western sectors are cooler than the central one.
The surface temperature evolution is fully determined
by annual harmonics. Our results do not confirm the
conventional view that the east shallow part of lake is
warmest and consequently evaporates more water
than other parts of lake. Thus, Sandoval’s (1994)
proposal to reduce water evaporation by cutting off
the east part of lake (supposedly the main area of
evaporation) has no scientific base. Apparently it is
necessary to rely on other alternatives to stabilize the
lake’s water level; for example, supply the Chapala
Lake with water from other river watersheds.
The El Nino 1997–98 event was the most severe of
this century, as many authors agree. The phenomenon
I. Tereshchenko et al. / Journal of Hydrology 264 (2002) 133–146144
caused the mean global temperature in the atmosphere
to increase. (Magana et al., 1999; Karl et al., 2000).
Our research has shown that this El Nino drastically
changed the temperature patterns not only along the
Pacific coast of Mexico, but also within a significant
distance from it. In the area of Chapala Lake the
annual atmospheric temperature course was intensely
modified during this El Nino. In the winter of 1997–
98, the mean temperature showed a negative anomaly
of 1 8C. However, in the summer of 1998 this
figure was positive, with a value of 1.5 8C in
comparison to 1996. Data analysis shows a
relationship between surface temperature vari-
ations and hydrometeorological characteristics
(temperature, evaporation, Lerma discharge and
lake level). The model we propose makes possible
the forecasting of the Chapala Lake mean surface
water temperature for any month of the year, both
for ‘normal years’ and El Nino years.
Acknowledgments
We would like to thank our colleagues from the
University of Guadalajara for their help in data
collection and processing, and especially to MSc.
Arturo Figueroa Montano for his help with the
Spanish to English translation. We also thank Erik
Marquez for the technical operative support in image
processing at ICML/UNAM. Finally, our thanks go to
the CUCEI, University of Guadalajara and CON-
ACYT (Mexico) for the financial support (Project
N33667-T).
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