Thursday, February 26, 2026

Crow is the Pilot

   Yes, the crow is a pilot, 

a passenger, a control tower


He does the work of the  control tower


No need for a black box, no petrol, but fuel is needed

Yesterday I. First the crow was eating a piece of bread and then

Pilot 


He planned where to fly


The food he eats is his food for his stomach and


And petrol is fuel.


How accurate is his vision? Flying in a moment


How difficult is life


How much energy does he get by eating?


How small is his brain but he has the strength to 

do the above tasks


Between a crow and a beggar, a crow is very good because he


Calls other friends with the food he gets

Wednesday, February 25, 2026

कावळा एक पायलट

 हो कावळा एक पायलट आहेत प्रवासी आहे कंट्रोल

 टॉवर चे काम तोच करतो

ब्लॅक बॉक्स ची गरज नाही पेट्रोल नाही पण इंधन लागते

कालच मी. पहिले कावळा कुरमुरे  वेचुन  खात होता आणि नंतर 

 पायलट महाशय

उडाले कुठे जायचे ते  प्लान स्वतः कडे 

खाण्यात त्याच्या आलेले अन्न हेच त्याच्या पोटासाठी पोटपणी आणि 

आणि पेट्रोल समान इंधन.

किती अचूक दृष्टी धोके दिसता क्षणात उडणे 

खरच किती अवघड जीवन

किती खाऊन उडण्याची ऊर्जा येत असेल ?

मेंदू किती छोटा पण वरील कामे करण्यास ताकद असणारा

कावळा आणि भिकारी यात कावळा हा खूप चांगला कारण तो

मिळालेले खाद्य इतर दोस्तांना बोलावून देणारा



Saturday, February 14, 2026

इडली मार्केटिंग

 हो इडली मार्केटिंग केली जाते

काही वर्षे झाली अंदाजे  50 वर्षाहून अधिक काळ

मार्केटिंग स्टाईल आगळी वेगळी होती

कोणी इडली घेता का? आरोग्यास चांगली

अशा घोषणा नाहीत

रस्ताने हे विक्रेते फिरत पण तोंडाला आराम देऊन विक्री चांगली होत असे आज ही होते

काही एक रबराचा हॉर्न वाजवून तो ही हाताने तोंडाला आराम  ग्राहक बोलावी ते ठराविक आवाज आल्या. वर नवीन पोजिशन केली आज ही पध्दत आहे.

पाव  वाला पाव पाव आवाज देतो सायकल ने फिरतो

धार वाला धार् वाला म्हणतो

जूने समान वाला समान जून पुराणे घेतो असा आवाज देतो

आवाज ही गरज आहे ती बासरी विकणाऱ्याला  बासरी घेऊन

तीच बासरी ते गण आपण नाही गाऊ शकत




Tuesday, February 10, 2026

Effect of Air Pollution and Neurological Dsease


 


Ref

Front Public Health. 2022 Jul 14;10:882569. doi: 10.3389/fpubh.2022.882569

The Physiological Effects of Air Pollution: 

Particulate Matter,

 Physiology and Disease

Jack T Pryor 1,2, Lachlan O Cowley 1, Stephanie E Simonds 1,*


Abstract

Nine out of 10 people breathe air that does not meet World Health Organization pollution limits. 

Air pollutants include gasses and particulate matter and collectively are responsible for ~8 million annual deaths.

 Particulate matter is the most dangerous form of air pollution, 

causing inflammatory and oxidative tissue damage. 

A deeper understanding of the physiological effects of particulate matter is needed for effective disease prevention and treatment.

 This review will summarize the impact of particulate matter on physiological systems, and where possible will refer to apposite epidemiological and toxicological studies. By discussing a broad cross-section of available data, 

we hope this review appeals to a wide readership and provides some insight on the impacts of particulate matter on human health.


Particulate Matter

Particulate matter (PM) are solid compounds suspended in air that are sufficiently small to be inhaled (Figure 1)

. PM is categorized by particle diameter (measured in μm); PM0.1, PM2.5 and PM10 whilst 

ambient concentration is usually quantified as μg/m3.

 Some PM are of natural origin (bushfires, dust, sea spray, aerosols, etc.) but anthropogenic PM (diesel, coal and biomass combustion and emissions from metal refineries etc.) are the most dangerous to health (13).

 High atmospheric concentrations of human-made PM, and toxic and oxidative chemical characteristics render them disproportionately hazardous (13).

 Elemental and complex chemical species of PM are diverse, with surface shape, chemistry and charge impacted by emission source and environmental conditions. PM chemistry can change through reactions with other airborne PM and be affected by the oxidative effects of ozone and low ambient pH (14, 15).


Fig 1

To scale illustration of the relative sizes of PM10, PM2.5, and PM0.1. Representative macrophage and mitochondria are included to scale for

Reference






Fig1

Neurological Disease

Increased ambient PM concentration positively correlates with the incidence of Alzheimer's disease, Parkinson's disease, Multiple Sclerosis, dementia and autism spectrum disorder (Figure 2) (127)

. Long-term PM2.5 exposure significantly increased age adjusted risk of mortality and hospital admission for Alzheimer's disease, Parkinson's disease and non-Alzheimer's disease dementia (128). 

This study found the strongest correlation to exist between PM2.5 and Alzheimer's disease (128). One longitudinal study found that people living within 50 meters of a main road had a 12% greater chance of dementia diagnosis (129).

 PM2.5 exposure is linked to faster decline in new learning and immediate recall, as well as MRI-detected gray matter atrophy in brain areas vulnerable to Alzheimer's disease pathology (130).

 PM2.5 exposure has been linked to Alzheimer's specific cognitive impairments (CERAD score but not ABC score) however post-mortem analysis of neuropathology in the brains of Alzheimer's disease patients failed to reveal any link between PM2.5 exposure 10 years before death, and disease progression indicated by Braak stage (131)

. The impact of specific PM (including black carbon, organic matter, nitrate, sulfate, sea salt and soil) exposure on the rate of initial Parkinson's disease hospitalization in New York State was investigated. This study revealed that with each standard deviation increase in either nitrate or organic matter PM, the risk of hospitalizations increased 1.06-fold (132).


PM 0.1 can cross the blood brain barrier and cause inflammatory and oxidative tissue damage as well as microglial activation (133). 

Glutamatergic excitotoxicity is a common reported endpoint for acute PM induced pathophysiology in the central nervous system. PM has been found in neurons, glia, endothelium, choroid plexus ependymal cells, cerebrospinal fluid, nasal epithelium, and olfactory epithelium of individuals subjected to PM exposure (134).

 PM2.5 has been found to reduce nervous system expression of the tight junction proteins, zonula occludens 1 and 2 (135). 

This study found a compromised blood brain barrier permeable to macrophage infiltration, and nervous system tissue subject to glutamatergic excitotoxicity, triggered by macrophage-derived glutamate (135).

 In mice, PM2.5 has been shown to reach the olfactory bulb and induce microglial activation and glutamatergic excitotoxicity that could be blocked with the antioxidant N-acetylcysteine (136).


Alzheimer's disease is characterized by cortical and hippocampal amyloid-β plaque and tau tangle deposition. Amyloid-β plaque formation and gliosis underlie at least some of the cognitive deficits associated with 

AD progression (137).

 In a transgenic mouse model of Alzheimer's disease, exposure to diesel emission PM2.5 exacerbated amyloid-β plaque deposition, and increased astrocytosis and microgliosis. Additionally, elevated inflammatory cytokines including tumor necrosis factor, nuclear factor-α, interleukins 1β and 6, interferon-γ and macrophage inflammatory protein-3α were identified in the cortices of double transgenic mice (138).

 In a similar study, 13-week exposure to diesel exhaust PM also accelerated cortical amyloid-β plaque deposition, an effect associated with significant impairments to motor coordination (139). Parkinson's disease is caused by loss of dopaminergic neurons in the substantia nigra of the basal ganglia. Neuron loss results in diminished cortical input and associated behavioral and cognitive deficits. In a rotenone-induced mouse model of Parkinson's disease, PM2.5 exposure induced mitochondrial dysfunction, oxidative stress and apoptosis in the substantia nigra. In the same study, PM exposure also exacerbated motor and somatosensory deficits (140). 

Multiple Sclerosis (MS) is a progressive, demyelinating and neurodegenerative disease of the CNS. Short-term PM exposure is associated with increased MS hospital admissions and relapse (127). In a mouse model of lipophosphatidylcholine-induced demyelination, PM exposure impairs myelin repair and sustains astroglia and microglia dependent neuroinflammation. PM2.5 exposure to rats impaired spatial learning and memory, inquiring ability and sensory function, these changes were related to ultrastructural changes to mitochondria and myelin (141).

 Mice exposed to PM2.5 for 10 months developed structural hippocampal alterations including diminished apical spine density and dendritic branching of hippocampal neurons and behavioral studies revealed reduced spatial learning and memory impairments (142).

Sunday, February 8, 2026

Effects of Air Pollution and Endocrine Disease

 


Ref

Front Public Health. 2022 Jul 14;10:882569. doi: 10.3389/fpubh.2022.882569

The Physiological Effects of Air Pollution: Particulate Matter, Physiology and Disease

Jack T Pryor 1,2, Lachlan O Cowley 1, Stephanie E Simonds 1,*

Endocrine Disease

The known effects of cigarette smoke on reproductive and thyroid hormones provide indications of the risks associated with PM exposure.

 Cigarette smoke is a risk factor in Graves hypothyroidism and is associated with elevated plasma cortisol, aldosterone, adrenal androgens and impacts female fertility by increasing steroid hormone binding globulin and decreasing circulating free estrogens (83–86). 

Several PM species have been identified as endocrine disrupting chemicals (87).

 In humans PM exposure is linked to insulin resistance, elevated circulating adipokines, hypothyroidism and (mixed) estrogenic effects (88). 

Thyroid hormones triiodothyronine (T3) and thyroxine (T4) regulate metabolic rate, cardiovascular tone and promote growth rate during fetal development and early life (89).

 In humans, PM exposure is associated with decreased plasma T4 both in pregnant women and new-borns, as well as congenital hypothyroidism and reduced infant birth weight (90). 

Black carbon, ammonia, organic matter and nitrate PM species appear to have the strongest links to thyroid dysfunction (91–94). 

Effective insulin signaling is required for glucose homeostasis, and insulin resistance is closely associated with obesity and is a risk factor for the onset of type-2 diabetes (95).

 PM exposure is associated with insulin resistance and non-alcoholic fatty liver disease, driven by oxidative stress and dyslipidaemia (96, 97).

 Together these studies highlight the link between air pollution and metabolic diseases including diabetes. Of >106 chemicals to which gas and oil extraction workers are exposed, 21 have been shown to exert estrogenic, androgenic and/or steroidogenic effects (98).

 Some chemicals identified as impacting endocrine function include benzene, toluene, ethylbenzene xylene, mercury, polychlorinated dibenzodioxins (PBDDs) and several polycyclic aromatic hydrocarbons (PAH) (88, 98, 99).

 Atmospheric sources of PAHs are vehicle emissions and biomass and coal combustion. Low molecular weight PAHs are in gas phase whereas high molecular weight PAHs are bound to the surface of PM (100). PAHs are classed as endocrine disrupting compounds and have been found to both increase and decrease estrogen receptor mRNA expression and function (REF). Estrogenic dysfunction has been shown to be both direct at estrogen receptors and indirect via aryl hydrocarbon receptor (AhR) signaling (101, 102). 

PBDDs also exert endocrine effects via AhRs, and preclinical experiments have shown AhR-mediated effects of dioxin exposure to include weight loss, reproductive and developmental toxicity, tumorigenesis and immune system dysfunction (103). 

PM contains many metal elements, some of which interfere with estrogenic signaling by mimicking endogenous estrogens (104). Metalloestrogens include aluminum, selenium, antimony, arsenic (arsenite; NaAsO2), barium, cadmium, chromium, cobalt, copper, lead, mercury, nickel, tin and vanadium (vanadate; V2O5) (16, 104).


Obesity and Diabetes

In humans, the association between PM2.5 exposure and obesity is dependent on age, gender and socioeconomic demographic (105, 106).

 A growing body of evidence indicates that PM2.5 exposure is a risk factor for reduced skeletal muscle mass, obesity, diabetes and hypertension (107–109). 

Long-term PM exposure is associated with a high risk for type 2 diabetes, and road traffic-specific PM is correlated with an elevated risk (110). 

Increased incidence of type-2 diabetes remains when adjusted for age, body mass index (BMI), and socioeconomic status (111, 112). 

PM exposure is associated with higher levels of circulating complement factor 3 (C3c), and women with elevated plasma C3c are more susceptible to diabetes than those with low C3c (112). PM2.5 exposure is associated with a faster decline in insulin sensitivity during childhood and higher BMI by age 18 (113–115). 

The associated between PM exposure and hypertension is greater in overweight and obese children (116). In animal studies, exposure of rats to PM increased chocolate consumption whereas in chow-fed wild-type mice, 10-week PM2.5 exposure increased visceral fat mass, insulin resistance and adipose tissue inflammation (117, 118). In mice, short-term PM exposure increased food intake, fat mass and UCP-1 expression in brown adipose tissue (119). PM exposure also induced hypothalamic inflammation indicated by increased microglia density, increased toll-like receptor-4 and elevated inhibitory nuclear factor-kappa-B-kinase-epsilon expression (119). After 12 weeks of PM exposure, mice exhibited increased food intake and elevated fat mass and had lower energy expenditure. Mice had elevated levels of plasma leptin and insulin and increased Homeostatic Model Assessment for Insulin Resistance (HOMA-IR) indicators of insulin resistance (119). This same study also revealed that PM exposure decreased hypothalamic satiety markers, including reduced levels of phosphorylated STAT 3, and diminished proopiomelanocortin expression (119).


PM exposure to mice was found to induce hepatic oxidative stress, inflammation, negatively affect glucose tolerance and induce insulin resistance (96, 120). Interestingly PM exposure has been found to increase hepatic triacylglycerols, free fatty acids and cholesterol levels in female but not in male mice (96). In addition to insulin resistance, PM exposure has been shown to exert toxic effects directly on the pancreas (121). In a streptozotocin-induced mouse model of type-1 diabetes, PM from diesel exhaust fumes exacerbated pancreatic cell vacuolation and islet cell apoptosis, increased pancreatic amylase activity, increased expression of oxidative stress markers 8-isoprostane and superoxide dismutase and reduced levels of the antioxidant glutathione peroxidase (121). In a rat model of gestational diabetes PM exposure induced maternal pancreatic inflammation indicated by diminished pancreatic glucose transporter-2 expression (122).

Saturday, February 7, 2026

Air Pollution Particulate matter and Renal Dsease

Abstract

Nine out of 10 people breathe air that does not meet World Health Organization pollution limits. Air pollutants include gasses and particulate matter and collectively are responsible for ~8 million annual deaths. Particulate matter is the most dangerous form of air pollution, causing inflammatory and oxidative tissue damage. A deeper understanding of the physiological effects of particulate matter is needed for effective disease prevention and treatment. This review will summarize the impact of particulate matter on physiological systems, and where possible will refer to apposite epidemiological and toxicological studies. By discussing a broad cross-section of available data, we hope this review appeals to a wide readership and provides some insight on the impacts of particulate matter on human health.

Particulate Matter

Particulate matter (PM) are solid compounds suspended in air that are sufficiently small to be inhaled (Figure 1). PM is categorized by particle diameter (measured in μm); PM0.1, PM2.5 and PM10 whilst ambient concentration is usually quantified as μg/m3. Some PM are of natural origin (bushfires, dust, sea spray, aerosols, etc.) but anthropogenic PM (diesel, coal and biomass combustion and emissions from metal refineries etc.) are the most dangerous to health (). High atmospheric concentrations of human-made PM, and toxic and oxidative chemical characteristics render them disproportionately hazardous (). Elemental and complex chemical species of PM are diverse, with surface shape, chemistry and charge impacted by emission source and environmental conditions. PM chemistry can change through reactions with other airborne PM and be affected by the oxidative effects of ozone and low ambient pH ().

Figure 1.

Figure 1

To scale illustration of the relative sizes of PM10, PM2.5, and PM0.1. Representative macrophage and mitochondria are included to scale for 

Renal Disease

Human kidneys filter ~180 L of blood each day and are therefore vulnerable to PM exposure (). 

In people, PM2.5 exposure has been linked to an accelerated decline in glomerular filtration rate,

 diminished glomerular function during pregnancy, increased risks of chronic kidney disease, end stage renal disease, renal failure and chronic kidney disease mortality ().

 Human studies have also revealed that PM2.5 exposure to positively correlate with risk of albuminuria; a marker of glomerular disfunction ().

 A comparison of renal biomarkers in welders and office workers revealed that 

welders - exposed to much higher levels of PM2.5 that office worker controls –

 had elevated plasma markers of renal tubule damage; urinary kidney injury molecule-1 and neutrophil gelatinase-associated lipocalin (). 

Another study investigating the potential for tubule damage in humans revealed a 10 μg/m3 increase in PM2.5 exposure to be associated with increased nephritis hospital admissions ().

 PM2.5 exposure is associated with an elevated risk of adverse post kidney transplant outcomes, including acute rejection, graft failure and death (). 

A study specifically investigating the impact of PM on post-transplant outcomes found a 10 μg/m3 increase of PM2.5 to correlate with a 1.31-fold increase in the odds 

of transplant failure, a 1.59-fold increase in 

odds of delayed graft function and a 1.15-fold increase in all-cause mortality within 1 year of surgery (). 

A similar study revealed an increase of 1 μg/m3 in PM10 exposure to be associated with increased risk of biopsy proven rejection, graft failure and mortality ().

 Intratracheal exposure of PM2.5 to immunodeficient mice revealed no obvious renal histopathology. However, PM exposure was associated with elevated serum markers of renal damage including kidney injury molecule-1, cystatin C and uric acid. Moreover, 14-day PM exposure progressively increased renal concentrations of malondialdehyde, hydrogen peroxide, glutathione peroxidase, nuclear factor kappa-β, tumor necrosis factor-α, transcription factor protein-65, NADPH oxidase 4 and heme oxygenase-1 (). 

In rats, sub-chronic exposure of PM2.5 resulted in elevated plasma β-2-microglobulin and cystatin-C; serum markers of early-stage kidney damage (). 

PM exposure has also been found to induce histopathological lung damage, increase median blood pressure, increase urine volume and water consumption ().

Exposure of rats to diesel emission PM significantly reduced renal blood flow in controls and to a greater extent in rats with adenine-induced chronic kidney disease (). 

Similar work in a mouse model of adenine-induced CKD revealed that PM exposure elevated renal tumor necrosis factor-α, lipid peroxidation, reactive oxygen species, collagen deposition, necrotic cell counts, dilated tubules cast formation and collapsing glomeruli ().

 

वायू प्रदूषणाचे शारीरिक परिणाम:

संदर्भ

फ्रंटियर्स इन पब्लिक हेल्थ. २०२२ जुलै १४;१०:८८२५६९. doi: 10.3389/fpubh.2022.882569

वायू प्रदूषणाचे शारीरिक परिणाम:

कणरूप पदार्थ,

शरीरक्रियाविज्ञान आणि रोग

जॅक टी प्रायर १,२, लॅकलान ओ काउली १, स्टेफनी ई सिमंड्स १,*

सारांश

दहापैकी नऊ लोक अशा हवेत श्वास घेतात जी जागतिक आरोग्य संघटनेच्या प्रदूषण मर्यादेची पूर्तता करत नाही.

वायू प्रदूषकांमध्ये वायू आणि कणरूप पदार्थांचा समावेश होतो आणि ते एकत्रितपणे दरवर्षी सुमारे ८ दशलक्ष मृत्यूंसाठी जबाबदार आहेत.

कणरूप पदार्थ हे वायू प्रदूषणाचे सर्वात धोकादायक स्वरूप आहे,

जे दाहक आणि ऑक्सिडेटिव्ह ऊतींचे नुकसान करतात.

प्रभावी रोग प्रतिबंध आणि उपचारांसाठी कणरूप पदार्थांच्या शारीरिक परिणामांची सखोल माहिती असणे आवश्यक आहे.

हा आढावा कणरूप पदार्थांच्या शारीरिक प्रणालींवरील परिणामांचा सारांश देईल आणि शक्य असेल तेथे संबंधित महामारीविज्ञान आणि विषविज्ञान अभ्यासांचा संदर्भ देईल. उपलब्ध माहितीच्या विस्तृत पैलूंवर चर्चा करून,

आम्हाला आशा आहे की हा आढावा विस्तृत वाचकांना आकर्षित करेल आणि मानवी आरोग्यावर कणरूप पदार्थांच्या परिणामांबद्दल काही अंतर्दृष्टी प्रदान करेल.

कणरूप पदार्थ

कणरूप पदार्थ (PM) हे हवेत निलंबित असलेले घन संयुगे आहेत जे श्वास घेण्याइतके लहान असतात (आकृती १).

PM चे वर्गीकरण कणांच्या व्यासानुसार (μm मध्ये मोजले जाते) केले जाते; PM0.1, PM2.5 आणि PM10, तर

वातावरणातील सांद्रता सहसा μg/m3 मध्ये मोजली जाते.

काही PM नैसर्गिक उत्पत्तीचे असतात (वणवे, धूळ, समुद्राची फवारणी, एरोसोल इत्यादी), परंतु मानवनिर्मित PM (डिझेल, कोळसा आणि बायोमास ज्वलन आणि धातू शुद्धीकरण कारखान्यांमधून होणारे उत्सर्जन इत्यादी) आरोग्यासाठी सर्वात धोकादायक असतात (१३).

मानवनिर्मित PM ची वातावरणातील उच्च सांद्रता आणि विषारी व ऑक्सिडेटिव्ह रासायनिक वैशिष्ट्ये त्यांना असमान प्रमाणात धोकादायक बनवतात (१३).

PM च्या मूलद्रव्यीय आणि जटिल रासायनिक प्रजाती विविध प्रकारच्या असतात, ज्यांच्या पृष्ठभागाचा आकार, रसायनशास्त्र आणि प्रभार उत्सर्जन स्रोत आणि पर्यावरणीय परिस्थितीनुसार प्रभावित होतो. PM चे रसायनशास्त्र हवेतील इतर PM सोबतच्या प्रतिक्रियांमुळे बदलू शकते आणि ओझोनच्या ऑक्सिडेटिव्ह परिणामांमुळे व कमी वातावरणीय pH मुळे प्रभावित होऊ शकते (१४, १५).  आकृती १

PM10, PM2.5, आणि PM0.1 च्या सापेक्ष आकारांचे प्रमाणबद्ध चित्रण. संदर्भासाठी, प्रतिनिधी मॅक्रोफेज आणि मायटोकॉन्ड्रिया प्रमाणानुसार समाविष्ट केले आहेत.

संदर्भ

आकृती १

Figure 1.

.

Figure 1.





कृपया लक्षात घ्या की पुनरावलोकन लवकरच सुरू केले जाईल.