SciELO - Scientific Electronic Library Online

 
vol.8Uso de Aspirina® (Ácido Acetilsalicílico) en el rendimiento del grano del cultivo de maízSilicato de sodio y quitosano: Una alternativa para el control in vitro de Colletotrichum gloeosporioides aislado de papaya (Carica papaya L.) índice de autoresíndice de assuntospesquisa de artigos
Home Pagelista alfabética de periódicos  

Serviços Personalizados

Journal

Artigo

Indicadores

Links relacionados

  • Não possue artigos similaresSimilares em SciELO

Compartilhar


Revista bio ciencias

versão On-line ISSN 2007-3380

Revista bio ciencias vol.8  Tepic  2021  Epub 04-Out-2021

https://doi.org/10.15741/revbio.08.e884 

Original articles

Demands to the health sector front the manifestations of climate change in Jalisco

M.G. Garibay-Chávez1 

A. Curiel-Ballesteros1  * 

1 Universidad de Guadalajara. Instituto de Medio Ambiente y Comunidades Humanas, Programa de Salud Ambiental, México. Camino Ramón Padilla Sánchez No. 2100 Nextipac, Zapopan, Jalisco C.P.45200.


Abstract

Climate change has triggered health hazards that need to be identified and recognized in Jalisco state. A confirmed threat is the extreme maximum temperatures that lead to a necessary diagnosis of vulnerability and risk as a basis for the design and implementation of adaptation measures to current and future manifestations. The demands of attention of the health sector have increased since the period of time where there is the probability of presenting extreme temperatures and heat waves has increased from two months considered as normal to four months at present with an increase in mortality due to cardiovascular diseases and morbidity due to gastrointestinal infections, likewise, the temperature has increased by two months which promotes the increase of the population of mosquitoes that transmit dengue fever.

The above requires a response from the health sector, not only in hospital care, but also in the prevention of exposure through an early warning system in the presence of danger with an evaluation of such communication strategies to break and reverse the increase in damage to the health of the Jalisco state inhabitants, particularly the Tlaquepaque, Zapopan, Tonalá, Guadalajara and Puerto Vallarta urban areas which turned out to be the most vulnerable to climate change in Jalisco.

Keywords: Climate change adaptation; vulnerability; temperature extremes; mortality; morbidity

Resumen

El cambio climático ha detonado peligros para la salud que requieren determinarse y reconocerse en Jalisco. Un peligro confirmado son las temperaturas máximas extremas que lleva a un necesario diagnóstico de la vulnerabilidad y de riesgo como base para el diseño e implementación de medidas de adaptación ante manifestaciones actuales y futuras. Las demandas de atención del sector salud han aumentado a partir de verse incrementado el periodo de tiempo donde existe la probabilidad de presentarse temperaturas extremas y olas de calor pasando de dos meses considerado como normal, a cuatro meses en la actualidad con un incremento en mortalidad por enfermedades cardiovasculares y en morbilidad por infecciones gastrointestinales, de igual manera ha aumentado en dos meses la temperatura que favorece el incremento de la población de mosquitos transmisores de dengue.

Lo anterior requiere de una respuesta del sector salud, no solo en la atención hospitalaria, sino en la prevención de la exposición a través de sistema de alerta temprana ante la presencia de peligro con una evaluación de dichas estrategias de comunicación para detener y revertir el incremento de daño a la salud de los habitantes de Jalisco, en particular las áreas urbanas de Tlaquepaque, Zapopan, Tonalá, Guadalajara y Puerto Vallarta que resultaron ser las más vulnerables al cambio climático en Jalisco.

Palabras clave: Adaptación al cambio climático; vulnerabilidad; temperaturas extremas; mortalidad; morbilidad

Introduction

In 1992, the First Assessment Report of the Intergovernmental Panel on Climate Change (IPCC, 1992) was published, establishing short-term adaptation measures, the first of which concerned the development of policies and programmes for emergency response and disaster prevention and the development of comprehensive and detailed management plans to reduce the future vulnerability of populations. Lavell (2011) raises the basic hypothesis that Disaster Risk Management, the concepts and methods, practice and strategies it has developed have much to offer the field of Climate Change Adaptation.

In the Northern Hemisphere, where Jalisco is located, the continental mass of the planet and the highest greenhouse gas emissions predominate, so it has been shown that positive temperature anomalies are increasing (NOAA, 2021).

The greatest uncertainty present in this changing climate, is in the effects that the increase of heat will have, since it has been confirmed that when human beings are exposed to temperatures outside their thermoneutral zone, it has effects on physical and mental health; going outside that zone and according to the vulnerability of the organism, can present diverse conditions of risk. The environmental thermoneutral zone or comfort zone of humans ranges from 24 to 31 °C (Gordon, 2005).

The Jalisco State Development Plan 2013-2033 warns that the state is vulnerable to climate change (Gobierno de Jalisco, 2013); and the citizen perception consultation included in the Jalisco State Climate Change Action Plan (PEACC) (Alcocer et al., 2014), indicates that the main word that defines climate change according to local respondents is “heat”.

The annual incidence of heat extremes is more frequent in metropolitan areas, and the rate of increase of such events is higher in expanding areas compared to smaller ones (Stone et al., 2010; EM-DAT, 2020).

In the document Mexico Fifth National Communication to the United Nations Framework Convention on Climate Change (SEMARNAT & INECC, 2012), it refers to the fact that acute diarrheal diseases, dengue, malaria and heat stroke are on the increase, identifying the urgency of carrying out greater efforts and effective measures by the health sector to reduce their impact on the population, and to be able to face up to lower costs in damages and lives.

Heat waves and extreme temperatures are recognized as a trigger for mortality and deaths from diseases of the circulatory system (I00-I99) in the Guadalajara metropolitan area, and identify as the most vulnerable groups of the population people of the male gender between 60 and 69 years of age (Estrella, 2017).

Jalisco is a territory where vulnerability to climate change is expressed in a wide diversity of variables and the potential damage it can cause in human lives is very high. Some of the vulnerability factors that contribute with the level of damage of the climate change-related events are: population density (in its two extremes high concentration and dispersion), dispersed and unplanned urban growth, lack of basic services in housing such as water and electricity (coverage gaps), illiteracy (their attention is a crucial factor for understanding the problem and its causes, changes in behavior and harm reduction), lack of basic knowledge of the inhabitants about climate change (which limits the recognition of it as a problem and the implementation of measures to prevent and better face its consequences), access to health (there is a third of the inhabitants of Jalisco who do not have social security), and poverty (the large urban centers concentrate most of the poor people in the state). Similarly, the capacities for adaptation require increasing human resources and civil protection infrastructure according to the demands for attention to the priority threats present in the state (Garibay & Curiel, 2015).

It is known that a quarter of the state territory is very sensitive to global warming. During the period 2000-2019, visible disasters in Jalisco have become frequent: epidemics (2009, 2008, 2007, 2005, 2003, 2019), floods (2006, 2007, 2008, 2003) and storms (2008), but nonvisible ones, such as heat waves (2002, 2003, 2005, 2013, 2018), have also increased. The municipalities where the greatest climatic disasters have occurred are: Guadalajara, Puerto Vallarta, Cihuatlán, Lagos de Moreno, Ocotlán, Tlaquepaque, Zapopan and Tlajomulco de Zúñiga (Garibay & Curiel, 2015).

Of the 12 main causes of morbidity considered as a consequence of climate change by The Interagency Working Group on Climate Change and Health (Portier et al., 2010) half are present in Jalisco according to analyses made with data from the Ministry of Health: Acute respiratory infections (21 444/100 000 inhab.); Intestinal infections (4 047/100 000 inhab.); intoxication by scorpion stings (615/100 000 inhab.); Arterial hypertension (652/100 000 inhab.); Asthma and asthmatic conditions (357/100 000 inhab.); and Pneumonia and bronchial pneumonia (307/100 000 inhab.) (Secretaría de Salud, 2020).

From a public health perspective, risk assessment is recognized as having many and varied forms as it is an essential component of human survival, and fundamental to the management of environmental health hazards (Fleming & Parker, 2015); a recognized definition of risk from this field is as the result of “the probability of exposure to a hazard leading to a negative consequence” (Ropeik & Gray, 2002). In this work, the hazard considered is extreme maximum temperatures and heat waves, as well as their effects on increased morbidity and mortality. In the risk approach, the predisposition to be negatively affected by a hazard is defined as vulnerability (IPCC, 2012); analyzing vulnerability makes it possible to determine the demands that can be made in the presence of hazards, the capacities that are or should be achieved, and the measures that need to be implemented so that the individuals who are at risk prevent, face and resist the threat scenarios with less damage (UNDP, 2010).

The National Academy of Science (2015) confirms that the world records thousands of additional premature deaths each year due to summer heat. Cardiovascular and respiratory diseases are commonly related to extreme heat, but the association is more complicated for diseases than for mortality.

According to the statistics reported by the Jalisco state Ministry of Health (2015), the groups of diseases that are increasing, firstly diseases of the circulatory system (I00-I99), in the year 2000 the mortality rate was 11.69 and by 2015 it presented 13.64 deaths per 10 000 inhabitants. Within this group are the ischemic heart diseases (I20-I25), which present an increasing trend, for the year 2000 the mortality rate was 5.30 and for 2015 7.08/10,000 inhab; the cerebrovascular diseases (I60-I69) observed a slight downward trend with a mortality rate for the year 2000 of 2.93 and 2015 of 2.74/10,000 inhab.

This work aims to make a diagnosis of vulnerability to climate change in the populations and human settlements of Jalisco that will serve as a basis for the design of adaptation measures in health.

Material and Mehods

The type of study is comparative and applied research in the public health framework. This is a quantitative, descriptive, retrospective and longitudinal study, which aims to determine how vulnerable the population is and how it is in terms of health in the presence of current manifestations and scenarios of climate change, who are and will be the most vulnerable and where is located.

From the epidemiological perspective, the model of ecological studies linked to the evaluation of attributable risk (Gordis, 2015) with retrospective analysis of historical meteorological and health records was considered. The attributable morbidity and mortality was estimated using the HIA methodology - Population Health Impact Assessment, recommended by the United Nations Environment Programme in the manual of methods for the assessment of human health impacts of climate change and adaptation strategies (UNEP, 1998).

The analysis period was from 2000 to 2014. The information was managed with the Jalisco Ministry of Health, the Jalisco Ministry of Environment and Territorial Development and the National Meteorological Service.

For the United Nations Environment Programme (UNDP, 2010), the disaster risk assessment considers seven steps:

  • Step 1. Understanding the current situation - through a review of the history of illnesses and deaths attributed to maximum temperature increases.

  • Step 2. Evaluation of the danger - from meteorological databases, considering maximum monthly temperatures, extreme daily temperature and heat waves.

  • Step 3. Exposure assessment to identify population at risk and disaster-prone areas - through morbidity and mortality statistics.

  • Step 4. Vulnerability analysis to determine the capacity to respond to the demand derived from the present dangers - with health, sociodemographic and economic indicators. For the aims of this diagnosis, urban localities with 2,500 or more inhabitants registered by the Instituto Nacional de Estadística y Geografía (INEGI, 2010) for the state of Jalisco were included. Vulnerability was determined considering the following indicators from INEGI and IIEG (2020) data: Population density (> 350 inhabitants/ha); Children ≤ 5 years old (> 35 children/ha); Adults ≥ 70 years old (> 12 older adults/ha); Illiterate (> 12 illiterate adults/ ha); Houses without potable water service (> 10 houses without potable water/ha); Houses without electric energy service (> 4 houses without electric energy/ha); Population without the right to health services (> 50,000) and Poverty (> 10,000 vulnerable people per income).

  • Step 5. Analysis of the loss of health in the exposed population, considering mortality rates per 10 000 inhabitants and morbidity for the 13 health regions of Jalisco - it was estimated that, given the increase in temperatures and heat waves, certain groups of the population will be more affected when they present conditions of vulnerability.

  • Step 6. Identify the risk reduction capacity - resulting from comparing the demand for care in a disaster (in this work it is referred to the increase in temperature) in a given population (urban localities of 2 500 or more inhabitants) in relation to the capacity that is available in health services coverage (health services beneficiaries).

  • Step 7. Formulation of strategies and action plans for the reduction of health losses (adaptation) - review of national and state plans and strategies.

Descriptive measures

Rate, Proportion, Mean, Attributable Risk, Correlation Coefficient, and Analysis of Variance.

Basic information

Morbidity and mortality databases (2000-2014) from the Jalisco Ministry of Health (Secretaría de Salud Jalisco, 2015); Data from the Population Census: Total Population 2000 to 2015, urban localities equal to or greater than 2,500 inhabitants of the state of Jalisco, from the National Institute of Statistics and Geography (INEGI, 2010); Meteorological data from 1965 to 2013 ERIC III from the Mexican Institute of Water Technology - Ministry of the Environment and Natural Resources (IMTA-SEMARNAT, 2013). Meteorological data from 1970 to 2014 from the Institute of Astronomy and Meteorology of the University of Guadalajara (IAM/UDG, 2015); Atmospheric monitoring data from 2000 to 2014 from the Ministry of Environment and Territorial Development of the State of Jalisco (SEMADET, 2020).

Evaluation criteria

For the meteorological data it was considered as a quality criterion that the station was located within the urban area and that it had continuous data in 80 % or more of the days of the study period. For mortality data, the causes were considered in the International Statistical Classification of Diseases and Related Health Problems, Tenth Revision -CIE 10- (OPS, 2018), avoiding those included in the “garbage code” list (Naghavi et al., 2010), that is, with an identification of ill-defined, unspecific causes or those that cannot be considered as basic causes of death.

Reliability Criteria

With respect to the definition and association of variables, a review of institutional sources such as the World Health Organization (WHO, 2021), the United Nations Environment Programme (UNEP, 2021) and the Center for Disease Control and Prevention (CDC, 2019) was considered; in addition to research journals with high visibility that address the issue of temperature, climate change and health: Environmental Health Perspectives and Epidemiology (Table 1).

Table 1 Matrix of variables and their operationalization. 

Conceptual variables* Operational definition Scales of measurement
Heat Wave. A long-lasting period with extremely high surface temperature. Heat wave duration. Number of consecutive days.
Peak Temperature. Manifestation of higher temperatures produced by changes in the course of the seasons. Maximum temperature reached. Temperature on the Celsius scale
Cardiovascular Diseases. Pathological conditions involving the cardiovascular system including the heart; the blood vessels; or the pericardium. Daily mortality Increased morbidity and mortality Number Rates, average, proportion, incidence.
Communicable Diseases. An illness caused by an infectious agent or its toxins that occurs through the direct or indirect transmission of the infectious agent or its products from an infected individual or via an animal, vector or the inanimate environment to a susceptible animal or human host. Daily mortality Increased morbidity and mortality Number Rates, average, proportion, incidence.
Mortality. All deaths reported in a given population. All-cause mortality. Annual all-cause mortality rate (per 10,000 inhabitants).
Morbidity. The proportion of patients with a particular disease during a given year per given unit of population. Registered patients per year Number of new cases of a disease

*Source: BIREME (2020).

Validity

The vulnerability assessment considered the methodological contributions of the World Health Organization, the United Nations Development Programme, the United Nations Environment Programme, the World Meteorological Organization, and the Social Studies Network on Disaster Prevention in Latin America (LA RED).

Results and Discussion

Hazard assessment

Analyzing the maximum temperature of 30 years (1970-1999) in the sites of greater concentration of the population of the state, it was observed that the monthly normal of maximum temperature presented its higher values in the months of April and May with greater probability of presence of temperatures of risk to the health, with data above 29 °C. The risk season has been extended in the period 2000-2015 from two to four months: March, April, May and June.

The years 2002 and 2003 presented the greatest positive anomaly of maximum temperatures above 3 °C, while 2004 registered the smallest value with a positive anomaly of 0.1 °C. The highest positive anomaly of maximum monthly temperature for the month of March was 4.8 °C in 2002; April 4.6 °C in 2001; 3.8 °C for May 2003 and 3.7 °C for June 2005. It is noteworthy that the highest temperature anomaly in 2002 and the lowest in 2004 was found in all the local weather stations with data that meet quality criteria located within urban areas.

For the daily extreme temperature evaluation, the two record years of positive maximum temperature anomaly (2002 and 2003) were analyzed, where the highest average correlation between maximum temperature and mortality from cardiovascular diseases was obtained at 36 °C (97th percentile), with a correlation of 0.34, indicating that exposure to these temperatures determines an increase in mortality from this cause, by 11 %.

From 2000-2014, heat waves occurred in 87 % of the years analyzed; in 2004 and 2014 they did not occur. Of the years with heat waves, in 54 % of them the maximum temperature was less than 36 °C, being the years from 2006 to 2010, 2012 and 2013.

The greatest estimated risk occurred in 46 % of the years with heat waves with extreme temperatures of 36 °C or more. The year 2002 recorded two heat waves, one of 27 days (April 17 to May 13) and another of 7 days (May 20 to 26); followed by 2001 with a 24-day wave (April 1 to 24); 2003 with 23 days (May 1 to 23); 2011 with 20 days (May 12 to 31); 2000 with 15 days (April 17 to May 1) and 2005 with 11 days (June 1 to 11).

Exposure assessment and population at risk

Gender differences were found with respect to heat exposure and death from cardiovascular disease, with a higher relative risk for males (5.57) than females (4.91).

Vulnerability analysis

Jalisco has 70 895 hectares with predominant use of human settlements, in which 87 % of the state population is concentrated, 60.3 % resides in the metropolitan area of Guadalajara (Guadalajara, Zapopan, Tlaquepaque, Tonalá, El Salto, Tlajomulco de Zúñiga and Ixtlahuacán de los Membrillos).

Of all the locations analyzed, those referred to the Guadalajara metropolitan area are those that show critical conditions in all the vulnerability indicators, so in terms of this methodology the most vulnerable settlements could be considered.

Vulnerability in the high category is found in the following municipalities/indicator:

By high population density: Guadalajara, Zapopan, Tlaquepaque, Tlajomulco de Zúñiga, El Salto, Tonalá, Lagos de Moreno and Puerto Vallarta.

Children ≤5 years old: Guadalajara, Tlaquepaque, Zapopan, Tonalá, Puerto Vallarta and Tlajomulco de Zúñiga.

Adults ≥70 years old: Guadalajara, Zapopan, Lagos de Moreno, Tlaquepaque and Jalostotitlán.

Illiterate: Guadalajara, Zapopan, Tlaquepaque, Tonalá, Puerto Vallarta.

Houses without drinking water service: Tonalá, Zapopan, Tlaquepaque, El Salto.

Homes without electricity service: Tonalá, Zapopan, Tlaquepaque, Puerto Vallarta and La Barca.

Population without the benefit of health services: Guadalajara, Zapopan, Tlaquepaque, Tonalá, Puerto Vallarta and El Salto.

Poverty: Guadalajara, Zapopan, Tlaquepaque, Tlajomulco de Zúñiga, Tonalá, Puerto Vallarta and Lagos de Moreno.

The above confirms that the greatest vulnerability in Jalisco is presented in its most critical condition in the metropolitan municipalities, which coincides with the importance being given at a global level to generate better adaptation measures to face climate change and climate variability, prioritizing the cities, first because the greatest amount of population is concentrated in them; They exhibit growth dynamics without planning and evaluation of the impact of the risks to health and life that this generates, they show the greatest number of people without coverage of basic services and poverty, and the response capacities at the individual and institutional levels are not being sufficient to face the demands related to climate change.

Analysis of the loss of health in the exposed population

Mortality

Considering the annual mortality rate in Jalisco in the period of study (2000-2014), it can be noted that the years 2002 and 2003 are above the trend and that 2004 shows a considerable decrease. During this period, an increase in mortality rates was observed, from 46 to 51 deaths per 10,000 inhabitants.

Figure 1 confirms that the annual mortality rate was higher than the trend line in the three years with positive maximum temperature anomalies with values above 2.5 °C, while in the years with anomalies <1 °C, it was below the trend line. Given the trend scenarios of climate change where positive maximum temperature anomalies will be seen more frequently, it is expected that there will be an increase in mortality rates in Jalisco.

Figure 1 Annual mortality rate behavior per 10 000 inhabitants in Jalisco during 2000-2014. 

Morbidity

Determination of the health burden of climate-sensitive diseases or events, taking into account the locations most vulnerable to maximum temperature increases.

In Table 2 it is noticeable how the intestinal infections by other organisms and the poorly defined ones (A04- Other intestinal bacterial infections-; A08- Intestinal infections due to viruses (except rotavirus) and other specified organisms- and A09- Diarrhea and gastroenteritis of presumed infectious origin-.) follow a pattern where the highest medical consultations occur in years with positive maximum temperature anomaly, which is very different in years close to normal.

Table 2 Cases of illnesses that present a greater sensitivity to anomalies of maximum temperatures in Guadalajara. 

Years with positive temperature anomaly Years with normal temperature
Illnesses 2002 2003 2011 2004 2007 2014
Intestinal infections by
other organisms and
those poorly defined.
137 143 127 778 130 016 110 831 108 586 120 319

Source: Own elaboration from the morbidity database, Department of Epidemiology, Jalisco Ministry of Health, 2000-2014 (Secretaría de Salud Jalisco, 2015).

To confirm the statistical significance of this difference between abnormalities, analysis of variance (ANOVA) was performed for all health regions by studying the pattern of intestinal infections. The Region 13 - Guadalajara- resulted with the highest statistical significance, followed by the Region 11 -Tonalá-, also with significant differences.

The Guadalajara sanitary region presented an annual difference of 18,400 medical consultations for intestinal infections in years with positive anomaly >2.5 °C with respect to those that registered <1 °C (which represented more than 50 consultations per day), and the Tonalá region with a difference of 3,711 medical consultations for intestinal infections per year (on average 10 additional consultations per day) (Table 3).

Table 3 Differences in the number of consultations for intestinal infections by other organisms and those poorly defined in years with differences in temperature anomalies. 

Sanitary
region
Positive temperature anomaly Normal temperature Ratio of
variances
Mean SD Min Max Mean SD Min Max
Guadalajara 131646 3993 127778 137143 113245 5085 108586 120319 16.20*
Tonalá 21643 962 20593 22917 17932 1235 16932 19672 11.23*
Zapopan 38872 4002 33369 42768 33610 949 32346 34633 3.27
Tlaquepaque 21435 4085 16050 25940 19465 1766 16984 20948 0.39

Source: Own elaboration from the morbidity database, Department of Epidemiology, Jalisco Ministry of Health, 2000-2014 (Secretaría de Salud Jalisco, 2015).

It is important to consider that in the assessment of risk of disease burden, intestinal infections are related to exposure to contaminated water, this is important, because the years that had the greatest positive anomaly of maximum temperature, were also years with more intense rainfall which causes flooding. Furthermore, in the case of the Tonalá Region, it is one with the highest indexes of surface water contamination.

To separate the effect of both phenomena (temperature and intensity of rain), the ANOVA was calculated considering only the hot months, without rain (April-June), finding a statistical significance (ratio of variances: 20.83).

Even if there is no statistical significance to consider that climate change is influencing the increase of other diseases, it is important to continue with prevention and monitoring measures for some groups of diseases, for example, vector-borne diseases. Several studies have shown that mosquitoes are extremely sensitive vectors to climate change. In 2009, Guadalajara registered 4,045 confirmed cases of dengue, one of the highest in the country, in a period from May 10 to December 19, with most cases occurring between August 23 and September 12. In 2019, this phenomenon occurred again and according to data from the Ministry of Health, Jalisco topped the list nationally for dengue cases with 11,727 cases (incidence of 141/100,000 inhabitants) (Secretaría de Salud, 2020). But perhaps most importantly, it is recognized that in temperatures higher than 13 °C mosquitoes hatch (Hopp & Foley, 2001). This is important, if we consider that the minimum temperatures in Guadalajara have been increasing, there is less cold, which represents an increase of 63 days per year with activity of the mosquito vector Aedes aegypti and the risk of exposure of the population.

Identify risk reduction capacity

In Jalisco it is identified in a trend scenario, that the increase of temperature (Figure 2) and heat waves, will cause an increase in mortality and morbidity, particularly those sensitive to changes in climate, such as cardiovascular diseases, intestinal infections by other organisms and poorly defined. Likewise, it is expected that those caused by vectors such as dengue fever will increase, including an increase in scorpion stings.

Figure 2 Increase in minimum temperatures from the normal period 1970-1999 and average 2000-2014 in Guadalajara. 

One way to reduce the risk is by decreasing the exposure of the population to dangerous temperatures, increasing information and knowledge of the effects that heat and climate changes have on health, risk communication, improving health protection against heat and climate variability through changes in behavior, food, technologies, constructions, green infrastructure, consumption patterns, cooling modules, public water troughs, surveillance, monitoring and research of diseases that are aggravated and triggered by heat, since many countries have increased the capacity to prevent diseases and deaths through decision-making based on information and knowledge, a greater interest in preparing human resources professionals in the health sector and public policies for risk reduction in the population and vulnerable sectors.

Formulation or review of strategies and action plans to reduce losses

Under current conditions, it is considered that the health sector in Jalisco should prepare for emergencies that may occur in contexts of climate change, since there are precedents regarding some events related to vector diseases where the response capacity has been complicated by demand. Faced with critical increases in diseases, a rapid, organized and coordinated response is required from the health sector, in the surveillance and warning of those that present high sensitivity to heat or propagation, diagnosis, attention to medical consultations, emergencies and control of sensitive diseases, availability of medicines and infrastructure, and number of doctors, nurses and beds per inhabitant, professionalization and preparation of medical personnel to precise diagnosis of diseases and effects of heat, medical units, research centers and specialized laboratories, emergency planning of the sector and authorities, and early warning systems and risk communication strategies and for self-protection appropriate for the population. Reducing the risk of disasters requires a health sector that is prepared and committed to acting to prevent disease and anticipate deaths.

Jalisco agrees with the IPCC (2012), that the maximum temperature is recognized as a reference of high confidence of climate change, so it should be considered as an indicator for monitoring the health sector.

The male gender presented greater health effects related to exposure to extreme temperature, which coincides with the report made by the CDC in the United States of America during 1999-2003 (CDC, 2006) and Bai et al. (2014) for China during 2011-2013.

The largest human settlements in Jalisco were found to be the most vulnerable in the state because of the high number of inhabitants exposed to the danger of extreme maximum temperatures, considering the indicators referred to: 1. Population density, as identified by Lavell (1996): the greater the number of people in a territory, the greater the damage possible in the presence of a hazard. 2. Children under 5 years old, also recognized by Yaron & Niermeyer (2004) as a vulnerable group in the face of rising temperatures and heat waves, pointing out that children lack thermoregulatory control, less sweating capacity and consequently the ability to dissipate heat, in addition to their limited ability to instinctively replace fluid loss or decrease their exercise in extreme heat. 3. Adults over 70 years of age in accordance with Medina-Ramón et al. (2006), who mention that older people are more susceptible to temperature extremes with more marked effects on heat, which may be explained in part by a decrease in their ability to thermoregulate and to detect temperature changes in their bodies. 4. Illiteracy, also identified by Bai et al. (2016) as a component that increases vulnerability to death or illness on days with high temperatures. 5. Population without access to health services, Likewise, Ebi et al. (2010) have pointed out when referring to those with limited access to medical care as a vulnerable group in terms of health in the face of climate change impacts. 6. Poverty, confirmed by the (United Nations, 2009) by pointing out that poor communities are the ones who face the greatest risk to climate-related disasters, have the greatest impacts and also the highest mortality. 7. Houses without drinking water service, similar to what was found by Inostroza et al. (2016) when they pointed out that access to drinking water is a variable that determines the capacity to adapt and vulnerability to heat, and that climate change adaptation measures in the most vulnerable areas should include improvements in the supply of drinking water. 8. Homes without electricity service, is confirmed by what Jessel et al. (2019) cited, who point out that energy insecurity in housing has serious implications for health, among which are the increase in morbidity and mortality rates of physical and mental illness during heat waves, in addition to not being able to implement adaptation measures such as having a refrigerator and air conditioning.

The findings on increased mortality from cardiovascular diseases related to increased maximum temperatures or prolonged periods of heat coincide with those reported by Medina-Ramón et al. (2006), regarding a greater marginal increase in mortality and those reported by Semenza et al. (1996), who refer that deaths from cardiovascular causes related to increased heat were also related to advanced age and pre-existing medical conditions. Therefore, future research should identify specific risk factors associated with these deaths.

With regard to morbidity from diarrhea and gastroenteritis of presumed infectious origin, the results found are consistent with research conducted on several continents. In Australia, Hall et al. (2011), found that at 7 °C the average temperature increased the probability of gastroenteritis by 4.6 %. Additionally, Lin et al. (2016), confirm in New York that for every degree Celsius increase in maximum temperature was significantly associated (0.7-0.96 %) with an increase in hospitalizations for gastrointestinal diseases. Finally, Zhou et al. (2013) identified in Shanghai that high temperatures were associated with an increased risk of diarrhea and gastroenteritis.

The Health and Climate Atlas published by the World Health Organization in collaboration with the World Meteorological Organization (2012) states that four infectious diseases are associated with climate change: malaria, diarrhea, meningitis and dengue fever. With respect to the last one, in Jalisco the temperature has increased, going from six months to the year as a period free of hatching of the mosquito transmitter of the dengue to only four months. The tendency presents us with a scenario where this control disappears and we have every day of the year temperatures with biological activity for this vector.

The level of progress made on the issue of climate change has allowed Jalisco to recognize the demands of the health sector in the face of temperature increases and heat waves. The factors that contribute to the vulnerability of urban human settlements must be prioritized in the design and implementation of adaptation strategies and actions.

Reducing the vulnerability of the Jalisco state urban human settlements must address critical aspects of development: poverty, illiteracy, deficiencies in health services, total coverage of water and energy services, (water and energy are necessary factors for temperature regulation and prevention of disease and death), since until progress is made, moving to other levels of attention to problems such as climate change will be more complex and efforts and results will continue to be limited.

Conclusions

In Jalisco the period of danger for exposure to extreme maximum temperatures has increased from two months (April-May) as a historical normal to four months (March-June). The maximum temperature above 36 °C (97th percentile) is considered the threshold to a high health hazard situation. The male gender in Jalisco is more vulnerable than the female gender to exposure to extreme maximum temperatures.

The greatest vulnerability is concentrated in urban settlements with a high number of inhabitants, with the most vulnerable population living in the Guadalajara metropolitan area. Mortality from cardiovascular diseases shows the greatest correlation with extreme maximum temperatures. The greatest statistical significance with the danger of maximum temperatures was presented for the morbidity by transmissible diseases considered by the Ministry of Health as intestinal infections by other organisms and those poorly defined in which are included the intestinal bacterial infections, intestinal infections due to virus (except rotavirus) and other specified organisms and the diarrhea and gastroenteritis of supposed infectious origin.

Although this study did not find a significant statistical association between the maximum temperatures and the presence of dengue, it was confirmed the increase of the minimum temperatures in more than 60 days per year with respect to the normal one, reason why it is considered an alert situation. The demands of the health sector that are visualized is to increase the surveillance and warning systems to the population of the diseases sensitive to the increase of temperature, which in a first stage would be those identified in this study.

REFERENCES

Alcocer, J.B.M., Ramírez, H.U. and Curiel, A. (2014). Plan Estatal de Acción ante el Cambio Climático (PEACC) del Estado de Jalisco. Universidad Autónoma de Guadalajara. https://www.gob.mx/cms/uploads/attachment/file/164931/2014_jal_peacc.pdfLinks ]

Bai, L., Ding, G., Gu, S., Bi, P., Su, B., Qin, D., Xu, G. and Liu, Q. (2014). The effects of summer temperature and heat waves on heat-related illness in a coastal city of China, 2011-2013. Environmental Research, 132: 212-219. https://doi.org/10.1016/j.envres.2014.04.002 [ Links ]

Bai, L., Woodward, A., Cirendunzhu and Liu, Q. (2016). County-level heat vulnerability of urban and rural residents in Tibet, China. Environmental Health, 15:(3), 1-10. https://doi.org/10.1186/s12940-015-0081-0 [ Links ]

BIREME-Latin American and Caribbean Center on Health Sciences Information. (2020). Virtual health library; Health Sciences Descriptors. PAHO, WHO. https://decs.bvsalud.org/es/Links ]

Centers for Disease Control Prevention [CDC]. (2006). Heat-Related Deaths United States, 1999 - 2003. https://www.cdc.gov/mmwr/preview/mmwrhtml/mm5529a2.htmLinks ]

Centers for Disease Control Prevention [CDC]. (2019). Climate and Health. https://www.cdc.gov/climateandhealth/policy.htmLinks ]

Ebi, K., Berry, P., Campbell-Lendrum, D., Corvalan, C. and Guillemot, J. (2010). Protecting Health from Climate Change. Vulnerability and adaptation Assessment. PHO/WHO. https://www.who.int/globalchange/publications/Final_Climate_Change.pdfLinks ]

EM-DAT, CRED. The International Disaster Database, Center for Research on the Epidemiology of Disasters. (2020). Disaster Profiles. Université Catholique de Louvain. https://www.emdat.be/Links ]

Estrella, L.E. (2017). Variabilidad climática y extremos de temperatura: efectos en la mortalidad por enfermedades del sistema circulatorio, Guadalajara, Jalisco 2000-2014 [Tesis de Maestría en Ciencias]. Universidad de Guadalajara. [ Links ]

Fleming, M.L. & Parker, E. (2015). Introduction to Public Health, 3rd Edition. Elsevier. [ Links ]

Garibay, M.G. & Curiel, A. (2015). Vulnerabilidad de los asentamientos humanos urbanos de Jalisco. En, A. Curiel, El Clima Cambiante, conocimientos para la adaptación en Jalisco. (pp. 61-77). Universidad de Guadalajara. https://www.researchgate.net/publication/304674384_El_Clima_Cambiante_Conocimientos_para_la_adaptacion_en_JaliscoLinks ]

Gobierno de Jalisco. (2013). Plan Estatal de Desarrollo Jalisco 2013 - 2033; Un plan de todos para un futuro compartido. Secretaría de Planeación y Participación Ciudadana. https://planeacion.jalisco.gob.mx/gestion-estrategica/planeacion/ped-2013-2033Links ]

Gordis, L. (2015). Epidemiología. Quinta edición. Elsevier Saunders. [ Links ]

Gordon, Ch. J. (2005). Temperature and Toxicology; An Integrative, Comparative, and Environmental Approach. CRC Press. [ Links ]

Hall, G., Hanigan, I., Dear, K. and Vally, H. (2011). The influence of weather on community gastroenteritis in Australia. Epidemiology & Infection, 139 (6): 927-936. https://doi.org/10.1017/S0950268810001901 [ Links ]

Hopp, M.J. & Foley, J.A. (2001). Global-Scale Relationships between Climate and the Dengue Fever Vector, Aedes Aegypti. Climatic Change, 48: 441-463. https://doi.org/10.1023/A:1010717502442 [ Links ]

Inostroza, L., Palme, M. and De la Barrera, F. (2016). A Heat Vulnerability Index: Spatial Patterns of Exposure, Sensitivity and Adaptive Capacity for Santiago de Chile. PLoS ONE, 11(9). https://doi.org/10.1371/journal.pone.0162464 [ Links ]

Instituto de Astronomía y Meteorología de la Universidad de Guadalajara [IAM/UDG]. (2015). Temperaturas Históricas.xlsx. (1970-2015). [ Links ]

Instituto de Información Estadística y Geográfica de Jalisco [IIEG]. (2020). Pobreza estadísticas; pobreza multidimensional por municipio 2010-2015. Gobierno de Jalisco. https://iieg.gob.mx/ns/?page_id=3786Links ]

Instituto Nacional de Estadística y Geografía [INEGI]. (2010). Censo de Población y Vivienda 2010. https://www.inegi.org.mx/programas/ccpv/2010/Links ]

Instituto Mexicano de Tecnología del Agua - Secretaría de Medio Ambiente y Recursos Naturales [IMTA-SEMARNAT]. (2013). Eric III Versión 3.2 extractor rápido de información climatológica [CD ROM]. [ Links ]

Intergovernmental Panel on Climate Change [IPCC]. (1992). Cambio Climático: Las Evaluaciones del IPCC de 1990 y 1992. Organización Meteorológica Mundial y Programa de Naciones Unidas para el Medio Ambiente. https://www.ipcc.ch/site/assets/uploads/2018/05/ipcc_90_92_assessments_far_full_report_sp.pdfLinks ]

Intergovernmental Panel on Climate Change [IPCC]. (2012). Managing the Risks of Extreme Events and Disasters to Advance Climate Change Adaptation. A Special Report of the Intergovernmental Panel on Climate Change. Cambridge University Press. https://www.ipcc.ch/report/managing-the-risks-of-extreme-events-and-disasters-to-advance-climate-change-adaptation/Links ]

Jessel, S., Sawyer, S. and Hernández, D. (2019). Energy, poverty and health in Climate Change: A Comprehensive review of an emerging literature. Frontiers in Public Health, (7):357. https://doi.org/10.3389/fpubh.2019.00357 [ Links ]

Lavell, A. (1996). Degradación Ambiental, Riesgo y Desastre Urbano. Problemas y conceptos: hacia la definición de una agenda de investigación. En: Fernández, M.A. (Comp.), Ciudades en Riesgo; Degradación Ambiental, Riesgos Urbanos y Desastres. La Red, Red de Estudios Sociales en Prevención de Desastres en América Latina. https://www.desenredando.org/public/libros/1996/cer/CER_cap02-DARDU_ene-7-2003.pdfLinks ]

Lavell, A. (2011). Desempacando la adaptación al cambio climático y la gestión del riesgo: Buscando las relaciones y diferencias: Una crítica y construcción conceptual y epistemológica. Elaborado en el marco del Proyecto UICN-FLACSO sobre Gestión del Riesgo y Adaptación al Cambio Climático. https://www.desenredando.org/public/varios/2011/2011_UICNFLACSO_Lavell_Adaptacion_Cambio_Climatico.pdfLinks ]

Lin, S., Sun, M., Fitzgerald, E. and Hwang, S.A. (2016). Did summer weather factors affect gastrointestinal infection hospitalizations in New York State?. Science of the Total Environment, 550: 38-44. https://doi.org/10.1016/j.scitotenv.2015.12.153 [ Links ]

Medina-Ramón, M., Zanobetti, A., Cavanagh, D.P. and Schwartz, J. (2006). Extreme temperatures and mortality: assessing effect modification by personal characteristics and specific cause of death in a multi-city case-only analysis. Environmental Health Perspectives. 114 (9):1331-1336. https://doi.org/10.1289/ehp.9074 [ Links ]

Naghavi, M., Makela, S., Foreman, K., O’Brien, J., Pourmalek, F. and Lozano, R. (2010). Algorithms for enhancing public health utility of national causes-of-death data. Population Health Metrics. 8 (9): 1-14. https://doi.org/10.1186/1478-7954-8-9 [ Links ]

National Academy of Sciences. (2015). Review of the Draft Interagency Report on the Impacts of Climate Change on Human Health in the United States. National Academies Press. https://www.nap.edu/download/21787Links ]

National Oceanic and Atmospheric Administration [NOAA]. (2021). Climate at a Glance, Global Time Series. U.S. Department of Commerce, National Centers for Environmental Information. https://www.ncdc.noaa.gov/cag/global/time-seriesLinks ]

Organización Panamericana de la Salud [OPS]. (2018). Clasificación Estadística Internacional de Enfermedades y Problemas Relacionados con la Salud Décima Revisión CIE - 10. Publicación Científica No. 554. https://iris.paho.org/bitstream/handle/10665.2/6282/Volume1.pdfLinks ]

Portier, C.J., Thigpen, K., Carter, S.R., Dilworth, C.H., Grambsch, A.E., Gohlke, J., Hess, J., Howard, S.N., Luber, G., Lutz, J.T., Maslak, T., Prudent, N., Radtke, M., Rosenthal, J.P., Rowles, T., Sandifer, P.A., Scheraga, J., Schramm, P.J., Strickman, D., Trtanj, J.M. and Whung, P.Y. (2010). A Human Health Perspective on Climate Change: A Report Outlining the Research Needs on the Human Health Effects of Climate Change. Environmental Health Perspectives/National Institute of Environmental Health Sciences. http://www.niehs.nih.gov/climatereportLinks ]

Ropeik, D. & Gray, G. (2002). Risk. A Practical Guide for Deciding What´s Really Safe and What´s Really Dangerous in the World Around You. Harvard School of Public Health. [ Links ]

Secretaría de Medio Ambiente y Desarrollo Territorial [SEMADET]. (2020). Bases de Datos de Calidad del Aire Anuales (2000 - 2014). SEMADET, Gobierno de Jalisco. http://siga.jalisco.gob.mx/aireysalud/descargas2020Links ]

Secretaría de Medio Ambiente y Recursos Naturales e Instituto Nacional de Ecología y Cambio Climático [SEMARNAT & INECC]. (2012). México Quinta Comunicación Nacional ante la Convención Marco de las Naciones Unidas sobre el Cambio Climático. http://cambioclimatico.gob.mx:8080/xmlui/handle/publicaciones/116Links ]

Secretaría de Salud, Dirección General de Epidemiología. (2020). Boletín Epidemiológico, Sistema Nacional de Vigilancia Epidemiológica, Sistema Único de Información 2019. https://www.gob.mx/salud/documentos/boletinepidemiologico-sistema-nacional-de-vigilancia-epidemiologica-sistema-unico-de-informacion-2019Links ]

Secretaría de Salud Jalisco, Departamento de Estadística. (2015). Bases de datos de Mortalidad 2000-2015. [ Links ]

Semenza, J.C., Rubin, C.H., Falter, K.H., Selanikio, J.D., Flanders, D., Howe, H.L. and Wilhelm, J.L. (1996). Heat-related deaths during the July 1995 heat wave in Chicago. The New England Journal of Medicine, 335:84-90. https://www.nejm.org/doi/pdf/10.1056/NEJM199607113350203Links ]

Stone, B., Jeremy, J.H. and Frumkin, H. (2010). Urban form and extreme heat events: are sprawling cities more vulnerable to climate change than compact cities?. Environmental Health Perspectives, 118(10):1425-1428. https://doi.org/10.1289/ehp.0901879 [ Links ]

United Nations Environment Programme [UNEP]. (1998). Handbook on Methods for Climate Change Impact Assessment and Adaptation Strategies. Version 2.0. UNEP y Vrije Universiteit Amsterdam.http://www.ivm.vu.nl/en/Images/UNEPhandbookEBA2ED27-994E-4538-B0F0C424C6F619FE_tcm234-102683.pdfLinks ]

United Nations Development Programme [UNDP]. (2010). Disaster Risk Assessment. https://www.undp.org/content/dam/undp/library/crisis%20prevention/disaster/2Disaster%20Risk%20Reduction%20-%20Risk%20Assessment.pdfLinks ]

United Nations Environment Programme [UNEP]. (2021). Climate Change (on line). https://www.unep.org/explore-topics/climate-changeLinks ]

United Nations. (2009). Risk and poverty in a changing climate, Invest today for a safer tomorrow; 2009 Global Assessment Report on Disaster Risk Reduction. UN, ISDR. https://www.preventionweb.net/english/hyogo/gar/report/index.php?id=9413&pid:34&pif:3Links ]

World Health Organization [WHO]. (2021). Climate Change (on line). https://www.who.int/health-topics/climatechange#tab=tab_1Links ]

World Health Organization and World Meteorological Organization (2012). Atlas of Health and Climate. WHO & WMO-No. 1098. https://apps.who.int/iris/handle/10665/112303Links ]

Yaron, M. & Niermeyer, S. (2004). Clinical Description of Heat Illness in Children, Melbourne, Australia-A Commentary. Wilderness and Environmental Medicine, 15: 291-292. https://doi.org/10.1580/1080-6032(2004)015[0291:CDOHI I]2.0.CO;2Links ]

Zhou, X., Zhou, Y., Chen, R., Ma, W., Deng, H. and Kan, H. (2013). High temperature as a risk factor for infectious diarrhea in Shanghai, China. Journal of Epidemiology, 23 (6): 418-423. https://doi.org/10.2188/jea.JE20130012 [ Links ]

Cite this paper: Garibay-Chávez, M.G., Curiel-Ballesteros, A. (2021). Demands to the health sector front the manifestations of climate change in Jalisco. Revista Bio Ciencias 8, e884. doi: https://doi.org/10.15741/revbio.08.e884

Received: December 02, 2019; Accepted: February 10, 2021

Creative Commons License Este es un artículo publicado en acceso abierto bajo una licencia Creative Commons