Indoor environment quality (IEQ) factors: Difference between revisions

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[[Category:Exposure-response functions]]
[[Category:Exposure-response functions]]
[[Category:Urgenche]]
[[Category:Urgenche]]
[[Category:Decision analysis and risk management]]
{{variable|moderator=Marjo|stub=Yes}}
{{variable|moderator=Marjo|stub=Yes}}


== Question ==
== Question ==


What established or possible indoor environment quality (IEQ) factors exist? What kind of dose-responses have been defined for them?
What established or possible indoor environment quality (IEQ) factors exist? What kind of exposure-response functions have been defined for them?


== Answer ==
== Answer ==


<t2b index="Exposure metric,Response,Response metric,Exposure route,Exposure unit,ERF parameter,Observation" locations="ERF,Significance,Description/Reference" unit="-">
==Rationale==
 
<t2b name='Indoor environment quality factors' index="Exposure agent,Response,Response metric,Exposure route,Exposure unit,ERF parameter,Observation" locations="ERF,Significance,Description/Reference" unit="-">
Visible dampness and/or mold or mold odor|Respiratory health effect||Inhalation|yes/no|OR|several, see Note 1||Note 1  
Visible dampness and/or mold or mold odor|Respiratory health effect||Inhalation|yes/no|OR|several, see Note 1||Note 1  
Dampness and/or mold|General health problem||perception|yes/no|increased risk of health problems %|64%||Evans et al (2000)
Dampness or mold, minimal|Mental health problems|Prevalence||yes/no|OR|1.39 (1.02-1.89)||Shenassa et al. 2007
Dampness and/or mold|Mental health problems||perception||OR|1.39(1.44-2.78)||Shenassa et al. 2007
Dampness or mold, moderate|Mental health problems|Prevalence||yes/no|OR|1.44 (1.08-1.92)||Shenassa et al. 2007
Dampness and/or mold|Self-assessed health poorer||Inhalation, Other?|||||Note 2
Dampness or mold, extensive|Mental health problems|Prevalence||yes/no|OR|1.34 (0.97-1.85)||Shenassa et al. 2007
Dampness and/or mold|Mental health problems||Inhalation, dermal and ingestion|yes/no|OR|1.76 (1.17-2.66)||Hopton and Hunt (1996)
Dampness and/or mold|Mental health problems|Prevalence||yes/no|OR|1.76 (1.17-2.66)|0.0056|Hopton and Hunt 1996
Chronic illness |Mental health problems||not applicable|yes/no|OR|1.99 (1.32-3.02)||Hopton and Hunt (1996)
Dampness and/or mold|Self-assessed health poorer|||||||Note 2
Living with children under 16 y |Mental health problems||not applicable|yes/no|OR|1.75 (1.15-2.68)||Hopton and Hunt (1996)
Living in a low income household |Mental health problems|Prevalence||yes/no|OR|1.61 (1.06-2.44)|0.0231|Hopton and Hunt 1996
Living in a low income household |Mental health problems||not applicable|yes/no|OR|1.61 (1.06-2.44)||Hopton and Hunt (1996)
Respondent unemployed|Mental health problems|Prevalence||yes/no|OR|1.55 (0.99-2.42)|0.0483|Hopton and Hunt 1996
Respondent unemployed |Mental health problems||not applicable|yes/no|OR|1.55 (0.99-2.42)||Hopton and Hunt (1996)
Living in flat instead of house|Morbidity|Morbidity||yes/no|RR|1.57||Fanning 1967
Living in flat instead of house|Upper respitory infection||Inhalation|yes/no||||D.Fanning (1967)
Floor of living|Psychoneurotic disorder|Incidence||1st vs. ground|RR|1.06||Fanning 1967 (RR calculated from Table 8)
Living in flat instead of house|Minor mental health problems||not applicable|yes/no||||D.Fanning (1967)
Floor of living|Psychoneurotic disorder|Incidence||2nd vs. ground|RR|1.74||Fanning 1967 (RR calculated from Table 8)
Living in flat instead of house|Morbidity||not applicable|yes/no|Increased morbidity (%)|57%||D.Fanning (1967)
Floor of living|Psychoneurotic disorder|Incidence||3rd vs. ground|RR|2.02||Fanning 1967 (RR calculated from Table 8)
Living in ground floor|Psychoneurotic disorder||not applicable|yes/no|Increased risk of psychoneurotic disorder (%)|6,3%||D.Fanning (1967)
Environmental tobacco smoke|Lung cancer|Morbidity|Inhalation|yes/no|RR|1.21 (1.13-1.30)||Note 7
Living in 1st floor|Psychoneurotic disorder||not applicable|yes/no|Increased risk of psychoneurotic disorder (%)|6,7%||D.Fanning (1967)
Environmental tobacco smoke|Ischaemic heart disease|Mortality|Inhalation|yes/no|RR|1.27 (1.19-1.36)||Note 7
Living in 2nd floor|Psychoneurotic disorder||not applicable|yes/no|Increased risk of psychoneurotic disorder (%)|10,9%||D.Fanning (1967)
Environmental tobacco smoke|Asthma|Morbidity|Inhalation|yes/no|RR|1.97 (1.19-3.25)||Age >21; Note 7
Living in 3rd floor|Psychoneurotic disorder||not applicable|yes/no|Increased risk of psychoneurotic disorder (%)|12,7%||D.Fanning (1967)
Environmental tobacco smoke|Asthma|Morbidity|Inhalation|yes/no|RR|1.32 (1.24-1.41)||Age <14; Note 7
Environmental tobacco smoke|Lung infections|Morbidity|Inhalation|yes/no|RR|1.55 (1.42-1.69)||Age <2; Note 7
Environmental tobacco smoke|Middle ear inflammation|Morbidity|Inhalation|yes/no|RR|1.38 (1.21-1.56)||Age <3; Note 7
Environmental tobacco smoke|Irritation of eyes and mucosa|||||||
Environmental tobacco smoke|Odour problems||Inhalation|||||
Environmental tobacco smoke|Comfort of housing|||||||
Environmental tobacco smoke|Chronic infections||Inhalation|||||
Wood smoke|Respiratory health effect||Inhalation|||||Note 3, Note 4
Wood smoke|Respiratory health effect||Inhalation|||||Note 3, Note 4
Wood smoke|Irritation of eyes and mucosa|||||||
Wood smoke|Irritation of eyes and mucosa|||||||
Line 34: Line 43:
Wood smoke|Chronic infections||Inhalation|||||
Wood smoke|Chronic infections||Inhalation|||||
Wood smoke|Cancer||Inhalation|||||
Wood smoke|Cancer||Inhalation|||||
Tobacco smoke|Respiratory health effect||Inhalation|||||
VOCs|Irritation symptoms|||||||
Tobacco smoke|Irritation of eyes and mucosa|||||||
CO2|Headache||Inhalation|||||
Tobacco smoke|Respiratory health effect|||||||
CO2|Tiredness||Inhalation|||||
Tobacco smoke|Odour problems||Inhalation|||||
CO|Headache||Inhalation|||||
Tobacco smoke|Comfort of housing|||||||
CO|Tiredness||Inhalation|||||
Tobacco smoke|Chronic infections||Inhalation|||||
Tobacco smoke|Cancer|||||||
VOCs|irritation symptoms etc.|||||||
CO2|headache, tiredness etc.|||||||
CO|headache, tiredness etc.|||||||
Insufficient air exchange|Headache|||||||
Insufficient air exchange|Headache|||||||
Insufficient air exchange|Tiredness|||||||
Insufficient air exchange|Tiredness|||||||
Line 62: Line 66:
Noise|Stress|||||||
Noise|Stress|||||||
Noise|Comfort of housing|||||||
Noise|Comfort of housing|||||||
Proximity to traffic|Mortality(?)|||||||
Proximity to traffic|Mortality|||||||
Radon|Lung cancer|||||||Note 5
Radon|Lung cancer|||||||Note 5
Relative humidity||||||||
Relative humidity||||||||
PM|mortality|||||||Note 3
PM2.5|Mortality|||||||Note 3
PM|chronic bronchitis|||||||
PM2.5|Chronic bronchitis|||||||
PM|lung cancer|||||||
PM2.5|Lung cancer|||||||
Reduced space (house/flat)|Depression|||||||Note 2
Reduced space (house/flat)|Depression|||||||Note 2
Reduced space (house/flat)|Mental health problems|||||||Note 2
Reduced space (house/flat)|Mental health problems|||||||Note 2
Reduced space (house/flat)|Self-assessed health poorer|||||||Note 2
Reduced space (house/flat)|Self-assessed health poorer|||||||Note 2
Garden|Depression|||||||Note 2
Access to garden|Depression|||||||Note 2
Floor level|Mental health problems|||||||Note 2
Floor level|Mental health problems|||||||Note 2
Overcrowding|Mental health problems|||||||Note 2
Overcrowding|Mental health problems|||||||Note 2
Overcrowding|Self assessed health poorer|||||||Note 2
Overcrowding|Self assessed health poorer|||||||Note 2
Sensory IAQ|Various health and well-being parameters|||||||
Sensory IAQ|Various health and well-being parameters|||||||
Maternal employment|Maltreatment of Children||Other|yes/no|OR|2.82 (1.59 - 5.00)||Sidebotham et al. 2002
Maternal employment|Maltreatment of children|Prevalence||no/yes|OR|2.82 (1.59-5.00)||Sidebotham et al. 2002
2 - 3 house moves in previous 5 years|Maltreatment of Children||Other|medium vs. low|OR|1.32 (0.77 - 2.27)||Sidebotham et al. 2002
No. of house moves in previous 5 years|Maltreatment of children|Prevalence||2-3 vs. 0-1|OR|1.32 (0.77-2.27)||Sidebotham et al. 2002
4 or more house moves in previous 5 years|Maltreatment of Children||Other|high vs. low|OR|2.81 (1.59 - 4.96)||Sidebotham et al. 2002
No. of house moves in previous 5 years|Maltreatment of children|Prevalence||4 or more vs. 0-1|OR|2.81 (1.59-4.96)||Sidebotham et al. 2002
Accomodation - overcrowed|Maltreatment of Children||Other|yes/no|OR|2.16||Sidebotham et al. 2002
Overcrowded accomodation|Maltreatment of children|Prevalence||yes/no|OR|2.16 (1.27-3.70)||Sidebotham et al. 2002
Accomodation - council|Maltreatment of Children||Other|Council vs. owned/mortgarged|OR|7.65||Sidebotham et al. 2002
Accomodation|Maltreatment of children|Prevalence||Council vs. owned/mortgarged|OR|7.65 (3.30-17.75)||Sidebotham et al. 2002
Accomodation - rented|Maltreatment of Children||Other|Rented vs. owned/mortgarged|OR|4.47||Sidebotham et al. 2002
Accomodation|Maltreatment of children|Prevalence||Rented vs. owned/mortgarged|OR|4.47 (1.82-10.98)||Sidebotham et al. 2002
Social Network Score < 21|Maltreatment of Children||Other|yes/no|OR|3.09 (1.84 - 5.19)||Sidebotham et al. 2002
Social Network Score < 21|Maltreatment of children|Prevalence||yes/no|OR|3.09 (1.84-5.19)||Sidebotham et al. 2002
Parental unemployement|Maltreatment of Children||Other|yes/no|OR|2.33||Sidebotham et al. 2002
Paternal employement|Maltreatment of children|Prevalence||no/yes|OR|2.33 (1.43-3.77)||Sidebotham et al. 2002
Car use|Maltreatment of Children||Other|yes/no|OR|2.23||Sidebotham et al. 2002
Car use|Maltreatment of children|Prevalence||no/yes|OR|2.33 (1.41-3.83)||Sidebotham et al. 2002
House dampness|Headache||inhalation, other|yes/no||||Packer et al. 1994
No. of deprivation indicators|Maltreatment of children|Prevalence||1 vs. 0|OR|9.58 (2.64-34.81)||Note 6; Sidebotham et al. 2002
House dampness|Aches and pains||inhalation, other|yes/no||||Packer et al. 1994
No. of deprivation indicators|Maltreatment of children|Prevalence||2 vs. 0|OR|23.44 (6.61-83.15)||Note 6; Sidebotham et al. 2002
House dampness|Diarrhea ||inhalation, other|yes/no||||Packer et al. 1994
No. of deprivation indicators|Maltreatment of children|Prevalence||3 vs. 0|OR|59.30 (17.52-200.76)||Note 6; Sidebotham et al. 2002
House dampness|Neurological problems||Other|yes/no||||Packer et al. 1994
No. of deprivation indicators|Maltreatment of children|Prevalence||4 vs. 0|OR|111.36 (32.31-383.801)||Note 6; Sidebotham et al. 2002
House dampness|Migraine||Other|yes/no||||Packer et al. 1994
House dampness|Problems in energy (according Nottingham Health Profile)|Prevalence||yes/no|OR|2.13||Packer et al. 1994 (OR calculated from Table 8)
House dampness|Chest problems||inhalation, other|yes/no||||Packer et al. 1994
House dampness|Social isolation (according Nottingham Health Profile)|Prevalence||yes/no|OR|2.04||Packer et al. 1994 (OR calculated from Table 8)
House dampness|High blood pressure||inhalation, other|yes/no||||Packer et al. 1994
House dampness|Problems in sleep (according Nottingham Health Profile)|Prevalence||yes/no|OR|1.50||Packer et al. 1994 (OR calculated from Table 8)
House dampness|Muscle tension||Other|yes/no||||Packer et al. 1994
House dampness|Problems in emotional reactions (according Nottingham Health Profile)|Prevalence||yes/no|OR|1.27||Packer et al. 1994 (OR calculated from Table 8)
Smoking|Respiratory disease||inhalation|yes/no||||Packer et al. 1994
House dampness|Problems in physical mobility (according Nottingham Health Profile)|Prevalence||yes/no|OR|1.37||Packer et al. 1994 (OR calculated from Table 8)
Social life|Health problems||other|<21||||Packer et al. 1994
House dampness|Perception of pain (according Nottingham Health Profile)|Prevalence||yes/no|OR|1.28||Packer et al. 1994 (OR calculated from Table 8)
Alcohol|Severe health problems||other|yes/no||||Packer et al. 1994
Smoking|Chronic respiratory disease|Prevalence|Inhalation|yes/no|OR|4.36 (2.46-7.74)|0.000|Blackman et al. 2001
Lone adult|Mental problems||other|yes/no||||Packer et al. 1994
Dampness|Chronic respiratory disease|Prevalence|Inhalation|yes/no|OR|2.10 (1.36-3.50)|0.004|Blackman et al. 2001
Unemployment seeking work|Mental problem||other|yes/no||||Packer et al. 1994
Unwaged household|Chronic respiratory disease|Prevalence||yes/no|OR|1.73 (1.24-2.41)|0.001|Blackman et al. 2001
Smoking|chronic respiratory disease||Inhalation|yes/no|OR|4.36(2.46-7.74)||Blackman et al. (2001)
Unsafe neighborhood|Mental health problems|Prevalence||yes/no|OR|2.35 (1.41-3.92)|0.001|Blackman et al. 2001
Dampness|chronic respiratory disease||Inhalation|yes/no|OR|2.10(1.36-3.50)||Blackman et al. (2001)
Draughts|Mental health problems|Prevalence||yes/no|OR|2.28 (1.41-3.69)|0.001|Blackman et al. 2001
Unwaged household|chronic respiratory disease||other|yes/no|OR|1.73(1.24-2.41)||Blackman et al. (2001)
Rehousing|Palpitations/breathlessness|Prevalence||yes/no|OR|0.71||Pettricrew et al. 2009 (OR calculated from Table 5)
Unsafe neighborhood|mental health problems||other|yes/no|OR|2.35(1.41-3.92)||Blackman et al. (2001)
Rehousing|Persistent cough|Prevalence||yes/no|OR|0.89||Pettricrew et al. 2009 (OR calculated from Table 5)
Chronic respiratory problems|mental health problems||other|yes/no|OR|2.35(1.50-3.69)||Blackman et al. (2001)
Rehousing|Painful joints|Prevalence||yes/no|OR|0.70||Pettricrew et al. 2009 (OR calculated from Table 5)
Draughts|mental health problems||other|yes/no|OR|2.28(1.41-3.69)||Blackman et al. (2001)
Rehousing|Faints/dizziness|Prevalence||yes/no|OR|0.68||Pettricrew et al. 2009 (OR calculated from Table 5)
Accommodation -large|Faints and dizziness|1.6|Other|yes/no|-5.7|||Pettricrew et al. 2009
Rehousing|Difficulty in sleeping|Prevalence||yes/no|OR|0.49||Pettricrew et al. 2009 (OR calculated from Table 5)
Accommodation -small|Palpitation, breathlessness|10.8|other|yes/no|-7.8|||Pettricrew et al. 2009
Rehousing|Sinus trouble/catarh|Prevalence||yes/no|OR|0.79||Pettricrew et al. 2009 (OR calculated from Table 5)
Drugdealing and taking|persistence cough|-11.0|Inhalation|yes/no|-2.1|||pettricrew et al. 2009
Housing tenure|Poor self-rated health|Prevalence||renter vs. owner|OR|1.48 (1.31-1.68)||Pollack et al. 2004
Housing dampness|painful joints|32.9|Inhalation|yes/no|-8.7|||Pettricrew et al. 2009
Noise from household|ear trouble|12.6|not applicable|yes/no|-5.7|||Pettricrew et al. 2009  
Noise from neighbours|difficulty in sleeping|8.6|not applicable|yes/no|-17.4|||Pettricrew et al. 2009
Speeding traffic|Sinus trouble, catarrh|-0.3|Other|yes/no|-4.7|||Pettricrew et al. 2009
Alcohol consumption|indigestion, stomach trouble|-6.3|ingestion|yes/no|-4.8|||Pettricrew et al. 2009
</t2b>
</t2b>
Accomodation owner |Stress||Inhalation|||||
Note 1 [[ERF of indoor dampness on respiratory health effects]]
Note 2 [http://heande.opasnet.org/wiki/Urgenche:_Workpackage_Exposure,_Health,_and_Well-being WP6 well-being report] (password-protected)
Note 3 [[ERF of PM2.5 on mortality in general population]]
Note 4 [[Concentration-response to PM2.5]]
Note 5 [[Health impact of radon in Europe]]
'''{{attack|# |Comments on Hopton and Hunt (1996):'''
*Row 5: Are you sure that the only possible exposure route is inhalation?
*Rows 6 to 9: Instead of "no", exposure route should be "not applicable".
*Rows 5 to 9: Use periods instead of commas as decimal points.|--[[User:Marjo|Marjo]] 10:22, 4 February 2013 (EET)}}
{{defend|# |Comments have been considered.|--[[User:Juho Kutvonen|Juho Kutvonen]] 13:52, 4 February 2013 (EET)}}
'''{{attack|# |Comments on Sidebotham et al. (2002)'''
*Rows 59, 66 and 67 are filled correctly. What comes to rows 60 to 65, small but essential changes should be done in columns "exposure metric" and "exposure unit". An example: "exposure metric" of row 60 should be "2 to 3 house moves in previous 5 years" and the respective "exposure unit" should be "medium vs. low". Based on this example, can you figure out the correct structures of rows 61 to 65?|--[[User:Marjo|Marjo]] 10:41, 4 February 2013 (EET)}}
{{defend|# |Good revisions, you have the right idea. However, some minor modifications would be appropriate: in row 62 "exposure unit" can simply be "yes/no", as the accomodation either is overcrowded or is not; no other possibilities exist. In row 65 the "exposure metric" should be "Social network score < 21" and "exposure unit" again simply "yes/no". |--[[User:Marjo|Marjo]] 15:44, 6 February 2013 (EET)}}
'''{{attack|# |Comments on Packer et al. (1994)'''
* In the paper of Packer et al. (1994) no ORs are given. Instead, they have measured prevalences. Therefore, "response metric" should be "prevalence" and "ERF parameter" should be "percentage unit change".
* Row 69: According the Table 4, "exposure metric" is damp housing and "response" is "smoking". Based on this, can you figure out the correct structures of rows 70 to 73? |--[[User:Marjo|Marjo]] 11:05, 4 February 2013 (EET)}}
{{comment|# |we updated the data|--[[User:Soroushm|Soroushm]] 23:25, 10 February 2013 (EET)}}
{{attack|# |I see that you have updated the data using the table 1. Unfortunately, that is not correct. You should update the data using tables 4 and 8, where relationships of dampness and various health-related endpoints are shown.|--[[User:Marjo|Marjo]] 15:27, 11 February 2013 (EET)}}
'''{{attack|# |Comments on Blackman et al. (2001)'''
*"Response metric" should describe how the response was measured: number of cases, incidence, prevalence,... I see that you have filled "response metric" boxes according earlier versions of this table, unfortunately, "response metric" was not used correctly there. The information you now have in boxes "response" and "response metric" all belongs to "response". You could do the following: decide and formulate the most accurate responses and put them into "response" -boxes and empty the "response metric" -boxes. If you can define the response metric, i.e. number of cases, incidence, prevalence etc.. used in the article, you can put it into "response metric" box. |--[[User:Marjo|Marjo]] 14:39, 4 February 2013 (EET)}}
{{attack|# |Don´t you think that the most likely exposure route in case of smoking and chronic respiratory disease as well as in case of dampness and chronic respiratory disease would be inhalation?|--[[User:Marjo|Marjo]] 16:31, 7 February 2013 (EET)}}
{{comment|# |Data tables updated, and correct, most likely exposure route to those exposure metrics would be inhalation|--[[User:Jukka Hirvonen|Jukka Hirvonen]] 09:11, 11 February 2013 (EET)}}
'''{{attack|# |Comments on Fanning (1967)'''
*This article does not express ORs, which makes it a bit tricky in terms of this exercise. Anyhow, the idea is to find numerical value for ERF to be added into table. At least for morbidity a numerical value can be found in the article, although it is not OR. Can you find it?
*If no numerical value can be found for the two other responses, they should be removed. Instead, you could try to put the data of Table VIII of the article into the IEQ table.
*Exposure route can not be "neurosis" or "common sickness". I suggest exposure route in these cases is "not applicable".
|--[[User:Marjo|Marjo]] 17:29, 8 February 2013 (EET)}}
{{attack|# |'''Comments on Petticrew et al. 2009'''
*You have both incorrect and correct parts here. Your "exposure metrics" are mostly wrong. I admit, this is tricky, as what you have written as "exposure metrics" could well be that. However, here "exposure metric" in all cases is "rehousing" for which a number of "responses" are described in tables 3,4,5 and 6. As there are so many responses, I suggest that you select only 6 of them to be included into the IEQ table above. Select those 6 responses you consider most interesting.
*Your article does not express ORs, instead prevalences and changes in them are given. Therefore, the "response metric" is here "prevalence" and "ERF parameter" is "percentage unit change".|--[[User:Marjo|Marjo]] 17:34, 11 February 2013 (EET)}}
{{defend|# |Correct parts include:
*"exposure unit"
*many of the responses and their values, however these values should be moved to column "ERF". For example, "painful joint" is a correct response, its "ERF parameter" is -8.7 as you have stated (but move this to the right place!). However, the respective exposure is not "housing dampness", instead it is here "rehousing", since the values are given in relation to it (table 5).|--[[User:Marjo|Marjo]] 17:34, 11 February 2013 (EET)}}
Thomasa and Joshuan ''''' Evans et al. (2000). <ref> Evans J, Hyndman S, Stewart-Brown S, Smith D, & Petersen S, (2000). An epidemiological study of the relative importance of damp housing in relation to adult health. J Epidemiol Community Health 2000;54:677–686..</ref>
An example for RefTag functionality:
'''''Pope et al. (2002) <ref>*Pope CA III, Burnett RT, Thun MJ, Calle EE, Krewski D, Ito K & Thurston KD (2002). Lung cancer, cardiopulmonary mortality, and long-term exposure to fine particulate air pollution. JAMA 287(9), 1132-1141.</ref>
john agyemang and emmanuel ''''' Shenassa et al. (2007). <ref>* Shenassa et al. (2007)Dampness and Mold in the Home and Depression: An Examination of Mold-Related Illness and Perceived Control of One’s Home as Possible Depression Pathways. America Journal of Public Health 2007 97(10): 1893–1899</ref>
Juho Kutvonen and Salla Mönkkönen '''''Hopton and Hunt (1996) <ref>*Hopton J.L. and Hunt S.M.(1996). Housing conditions and mental health in a disadvantaged area in Scotland. Journal of Epidemiology and Community Health 1996;50:56-61</ref>
Isabell Rumrich and Stefania Caporaso '''''Sidebotham et al. (2002) <ref>*Sidebotham et al. (2002). Child maltreatment in the “Children of the Nineties:” deprivation, class, and social networks in a UK sample.Child Abuse and Neglect 2002;26:1243-1259</ref>


Soroush Majlesi and Adnan Ahmad ''''' Packer et al. (1994) <ref>*Packer et al. Damp housing and adult health: results from a lifestyle study in Worcester, England.Journal of epidemiology and community health 1994;48(6):555–559</ref>
* Note 1 [[ERF of indoor dampness on respiratory health effects]]
* Note 2 [http://heande.opasnet.org/wiki/Urgenche:_Workpackage_Exposure,_Health,_and_Well-being WP6 well-being report] (password-protected)
* Note 3 [[ERF of PM2.5 on mortality in general population]]
* Note 4 [[Concentration-response to PM2.5]]
* Note 5 [[Health impact of radon in Europe]]
* Note 6 Indicators of deprivation: overcrowded accommodation, accomodation ownership, paternal employment, car use
* Note 7 [[ERF of several environmental pollutions]]


Jukka Hirvonen and Sami Rissanen ''''' Blackman et al. (2001) <ref>*Blackman T, Harvey J, Lawrence M & Simon A. (2001). Neighbourhood renewal and health: evidence from a local case study. Health & Place 7(2001), 93-103.</ref>
Niklas Holopainen and Kasperi Juntunen ''''' Fanning D. M. et al. (1967) <ref>*Fanning D. M. (1967). Families in flats. British Medical Journal 4(1967), 382-386.</ref>
Matthew Adeboye and Adedayo Mofikoya '''''Petticrew et al. (2009) <ref>*Petticrew et al. (2009). Quantitative and qualitative evaluation of the short-term outcomes of housing and neighbourhood renewal. BMC public health 2009;9:415</ref>


'''Precision and Plausability of Hopton and Hunt (1996)'''
'''Precision and Plausability of Hopton and Hunt (1996)'''


- Reporting bias: Perhaps ít´s difficult to use subjective data due to reporting bias. This is because people may answer in different ways or they don´t answer at all. In addition, people experience household conditions differently.{{defend|# |Good points.|--[[User:Marjo|Marjo]] 14:50, 4 February 2013 (EET)}}
- Reporting bias: Perhaps ít´s difficult to use subjective data due to reporting bias. This is because people may answer in different ways or they don´t answer at all. In addition, people experience household conditions differently.


- Possible confounding variables were controlled. {{comment|# |Can you give examples of the confounding variables mentioned in the paper?|--[[User:Marjo|Marjo]] 14:50, 4 February 2013 (EET)}}{{defend|# |Sociodemographic and economic variables, e.g. age and income. |--[[User:Juho Kutvonen|Juho Kutvonen]] 12:23, 6 February 2013 (EET)}}
- Possible confounding variables such as sociodemographic and economic variables, e.g. age and income, were controlled.  


- Selection bias: The sample is clearly not representative of the general population and therefore the analysis focuses on differences within the sample. Thus it´s worth considering if the results can be generalized to whole population.{{defend|# |Good points.|--[[User:Marjo|Marjo]] 14:50, 4 February 2013 (EET)}}
- Selection bias: The sample is clearly not representative of the general population and therefore the analysis focuses on differences within the sample. Thus it´s worth considering if the results can be generalized to whole population.




'''Precision and Plausability of Sidebotham et al. (2002)'''
'''Precision and Plausability of Sidebotham et al. (2002)'''


- Maltreatment is defined and measured as registration for physical injury, neglect, sexual abuse, emotional abuse. That way all maltreatments, which are not registred are not taken into account.
- Maltreatment is defined and measured as registration for physical injury, neglect, sexual abuse, emotional abuse. That way all maltreatments, which are not registered are not taken into account.
    
    
- The measurement of the social class is not too accurate, because  no allowance for nonworking mothers and no parental social class allocated for single mothers can be applied.  
- The measurement of the social class is not too accurate, because  no allowance for nonworking mothers and no parental social class allocated for single mothers can be applied.  


- The nature of relationship with child maltreatment is complex (confounder, cultural values, etc). That causes problems finding an association or causality between an exposure factor and maltreatment. Moreover, maltreatment has different definition in different cultural groups.  
- The nature of relationship with child maltreatment is complex (confounder, cultural values, etc). That causes problems in finding an association or causality between an exposure factor and maltreatment. Moreover, maltreatment has different definition in different cultural groups.  


- The parental income is not measured directly, but car ownership as a proxy indicator and the receipt of welfare payment are used.  
- The parental income is not measured directly, but car ownership as a proxy indicator and the receipt of welfare payment are used.  
Line 207: Line 143:
- Controlling for social factors was done.  
- Controlling for social factors was done.  


- Large amount of prospectively data are collected and used in in the study, which is a clear strength.
- Large amount of prospectively collected data are used in in the study, which is a clear strength.
   
   
- The participation is lower among the maltreated group, which might influence the outcome of the statistical analysis or bias the results of the study.  
- The participation is lower among the maltreated group, which might influence the outcome of the statistical analysis or bias the results of the study.  


- The risk of social bias and no way of measuring the effect of such bias. A social bias can be defined as a prejudgement of a specific social group. In this case, it might be that those, who collected the data might have expectations, that parents which lower or higher social background are more prone to maltreat their child and let this expectation influence their interpretation of the results. This is not very likely here, though, because all parameters which were used for the analysis can me measured and there is not much freedome for interpretation.  
- The risk of social bias and no way of measuring the effect of such bias. A social bias can be defined as a prejudgement of a specific social group. In this case, it might be that those, who collected the data might have expectations, that parents which lower or higher social background are more prone to maltreat their child and let this expectation influence their interpretation of the results. This is not very likely here, though, because all parameters which were used for the analysis can me measured and there is not much freedome for interpretation.  
{{comment|# |You have listed correct points that may affect precision and plausibility of the ERF; well done. However, it would be easier for the reader if you would use full sentences or otherwise would explain a bit more in detail how these issues affect the precision and plausibity of ERF.
*What is meant with "social bias" here?|--[[User:Marjo|Marjo]] 15:06, 4 February 2013 (EET)}}
{{comment|# |We added explanations.|--[[User:Isabell Rumrich|Isabell Rumrich]] 09:58, 7 February 2013 (EET)}}




Line 227: Line 158:
-      lifestyle: consumption of alcohol and smoking
-      lifestyle: consumption of alcohol and smoking


{{comment|# |It might be helpful for the reader if you would use full sentences in order to explain how the above issues affect the precision and plausibility of ERF. |--[[User:Marjo|Marjo]] 15:28, 4 February 2013 (EET)}}
-      it is still difficult to understand the housing condition because none of the studies are complete and detailed  so that direct comparison with the questions cannot be made and measurements of parameters, potential confounding factors as well as clear dose-response relationship should be adjusted for example physical effect of damp is responsible for muscle tension, backache and headache  but on the other hand the study poins out that there is a strong relationship between damp housing and adverse health impact. {{comment|# |I see that the two last points are in concordance with each other.|--[[User:Marjo|Marjo]] 15:28, 4 February 2013 (EET)}}


'''Precision and Plausability of Blackman et al. (2001)'''
'''Precision and Plausability of Blackman et al. (2001)'''


- Bias in respondents answers to realistically evaluate their and family members health.{{defend|# |Good.|--[[User:Marjo|Marjo]] 16:25, 7 February 2013 (EET)}}
- Bias in respondents answers to realistically evaluate their and family members health


- Some housings that where targets on first survey were demolished during second survey.
- Some housings that where targets on first survey were demolished during second survey.


- No data from comparison neighbourhood without renewal to back up observed health changes after renewal program. {{defend|# |Good point.|--[[User:Marjo|Marjo]] 16:25, 7 February 2013 (EET)}}
- No data from comparison neighbourhood without renewal to back up observed health changes after renewal program.  


- Relationship between dampness, draughts and mental health is uncertain, because the mechanism is unknown.{{defend|# |Again good, although you could specify this. Is it so that associations have been found but the mechanisms are unclear?|--[[User:Marjo|Marjo]] 16:25, 7 February 2013 (EET)}}
- Relationship between dampness, draughts and mental health is uncertain, because the mechanism is unknown


- Multivariate analysis using regression model was used to control variables, such as economic, housing, respiratory and mental health related to increase plausability{{comment|# |So in contrast to the previous points, this increases the plausibility of ERF, is this what you mean?|--[[User:Marjo|Marjo]] 16:25, 7 February 2013 (EET)}}
- Multivariate analysis using regression model was used to control variables, such as economic, housing, respiratory and mental health related to increase plausability which increases the plausibility of ERF.


{{comment|# |Precisions and plausabilities updated|--[[User:Jukka Hirvonen|Jukka Hirvonen]] 09:30, 11 February 2013 (EET)}}


'''Precision and Plausability of D. Fanning (1967)'''
'''Precision and Plausability of D. Fanning (1967)'''


-      The study is so old that the exposures and responses are real but the accuracy is quite poor. The basics are almost same as today but measurement techniques are so old that the results are not comparable to modern results. {{attack|# |Which specific measurement techniques do you mean? For example, they have measured first attendances by general practitioners, and I don´t think the accuracy of counting has changed significantly.|--[[User:Marjo|Marjo]] 18:08, 8 February 2013 (EET)}}{{defend|# |However, I agree with you that the oldness of study is a bit striking. Probably today many other parameters in addition to those used in the article would be measured when conducting this kind of study.|--[[User:Marjo|Marjo]] 18:08, 8 February 2013 (EET)}}
-      The study is quite old. Probably today many other parameters in addition to those used in the article would be measured when conducting this kind of study.


-      The study has considered the difference between children and adults.{{defend|# |Good point.|--[[User:Marjo|Marjo]] 18:08, 8 February 2013 (EET)}}
-      The study has considered the difference between children and adults.


-      The study has not considered the differences between different flats and houses. They have only categories for houses and flats but the differences between houses are not considered. This causes bias to the study.{{comment|# |Well, it is possible. However, it is always a question of e.g. resources how specific and detailed a study can be. Maybe they could more apparently mention whether there were any significant dissimilarities between houses. |--[[User:Marjo|Marjo]] 18:08, 8 February 2013 (EET)}}
-      The study has not considered the differences between different flats and houses. They have only categories for houses and flats but the differences between houses are not considered. This may cause bias to the study.  




Line 258: Line 185:
- Data collection at the three occassions in the intervention group before moving, one year after moving and 2 years after moving to the social housing gives strenght to the study in analysing changes in the housing circumstances and in neighbourhood.  
- Data collection at the three occassions in the intervention group before moving, one year after moving and 2 years after moving to the social housing gives strenght to the study in analysing changes in the housing circumstances and in neighbourhood.  


- Recruitment into the study was discussed by the landlord to the tenant once they accepted the housing offer which dosn't gives the RSL direct contact with the participant though this serves as a way of good recreuitments but it dose not guarantee the authenticity of the data collected. e.g RSL couldn't supply the number of people who refuse to participate in the study to the SHARP research team.
- Recruitment into the study was discussed by the landlord to the tenant once they have accepted the housing offer which dosn't gives the RSL direct contact with the participant though this serves as a way of good recruitments but it dose not guarantee the authenticity of the data collected. e.g RSL couldn't supply the number of people who refuse to participate in the study to the SHARP research team.


- Broad range of adult household categories in the intervention group which was used as a base for recruiting the comparism group stenghthen the study. (family households, with children under age of sixteen years, older households where the respondents and adult members of the households were of pensionable age, and adult households with a combination of relationships, including parents with children atleast 16 years of age, people unrelated to one and another and couples )
- Broad range of adult household categories in the intervention group which was used as a base for recruiting the comparism group stenghthen the study. (family households, with children under age of sixteen years, older households where the respondents and adult members of the households were of pensionable age, and adult households with a combination of relationships, including parents with children atleast 16 years of age, people unrelated to one and another and couples )
Line 264: Line 191:
- Qualitative and quantitative findings were only presented for 1 year(wave 2) in the study which dose not proof if the effects are sustained and probabely if differences in health outcomes occur at two years in the intervention and comparism groups.
- Qualitative and quantitative findings were only presented for 1 year(wave 2) in the study which dose not proof if the effects are sustained and probabely if differences in health outcomes occur at two years in the intervention and comparism groups.


- recollection bias may occur during interview if participant in the groups can not recall adequately past occurences relating to health, housing and neighbourhood questions.  
- recollection bias may occur during interview if participant in the groups if they can not recall adequately past occurences relating to health, housing and neighbourhood questions after one year and two years of movement to the new house.  


- Bias in subsequent analysis can also occur if there is any significant changes in the groups associated with self reported health.
- Bias in subsequent analysis can also occur if there is any significant changes in the groups associated with self reported health.
   
   
{{defend|# |Good points and thorough work! By checking the spelling you could increase the elegancy of your work.|--[[User:Marjo|Marjo]] 17:46, 11 February 2013 (EET)}}


'''Precision and Plausibility of Pollack et al. (2004)'''


The study controls some factors which can potentially cause bias in the result, like socioeconomic factors, relation to the neighbours and pollution of the local environment. However, the potential effects of working conditions on the health of the study subjects has not been addressed.       
In addition, it should be found out whether life style, diet, smoking, and use of alcohol are included it in socioeconomic factors.


=== Dependencies ===
===Indoor environment quality (IEQ) factors===
 
<t2b name='IEQ factors' index="Building,Heating,Observation" unit= "h-1,%,%,%,-,%,%,%,Bq/m3" locations="Ventilation rate,Dampness%,Smoking%,Biomass burning%,Indoor background emissions,In noise areas%,Too hot in summer%,Too cold in winter%,Radon" desc="Description" >
Detached houses|District|0.71 (0.3-1.12)|5-16.5|2.35 (1.4-3.4)|||15|||100 (95-105)|Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
Detached houses|Electricity|0.71 (0.3-1.12)|5-16.5|2.35 (1.4-3.4)|||15|||100 (95-105)|Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
Detached houses|Oil|0.71 (0.3-1.12)|5-16.5|2.35 (1.4-3.4)|||15|||100 (95-105)|Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
Detached houses|Wood|0.71 (0.3-1.12)|5-16.5|2.35 (1.4-3.4)|||15|||100 (95-105)|Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
Detached houses|Geothermal|0.71 (0.3-1.12)|5-16.5|2.35 (1.4-3.4)|||15|||100 (95-105)|Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
Row houses|District|0.71 (0.3-1.12)|5-16.5|2.35 (1.4-3.4)|||21|||100 (95-105)|Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
Apartment houses|District|0.71 (0.3-1.12)|5-16.5|2.35 (1.4-3.4)|||30|||100 (95-105)|Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
Leisure houses|Electricity||||||||||
Offices|District|||0|||||||Assumption
Commercial|District|||0|||||||Assumption
Health and social sector|District|||0|||||||Assumption
Public|District|||0|||||||Assumption
Sports|District|||0|||||||Assumption
Educational|District||24|0|||||||Haverinen-Shaughnessy et al. 2012; Assumption
Industrial|District|||0|||||||Assumption
Other|District||||||||||
</t2b>
 
Gens 2012 <ref>Gens 2012 [http://elib.uni-stuttgart.de/opus/volltexte/2012/7858/pdf/Diss_LK_final_version.pdf]</ref>
 
Haverinen-Shaughnessy 2010 <ref>Haverinen-Shaughnessy 2010 [http://www.nature.com/jes/journal/v22/n5/full/jes201221a.html]</ref>
 
Haverinen-Shaughnessy et al. 2012 <ref>Haverinen-Shaughnessy et al. 2012 [http://onlinelibrary.wiley.com/doi/10.1111/j.1600-0668.2012.00780.x/abstract;jsessionid=B4B14073001B07861216D517A0FAED1E.d01t01]</ref>
 
Turunen et al. 2010 <ref>Turunen et al. 2010 [http://www.ncbi.nlm.nih.gov/pmc/articles/PMC2996365/]</ref>


=== Formula ===


==See also==
==See also==
{{Urgenche}}
http://en.opasnet.org/en-opwiki/index.php?title=Indoor_environment_quality_(IEQ)_factors&oldid=29149


==Keywords==
==Keywords==

Latest revision as of 14:26, 27 February 2015



Question

What established or possible indoor environment quality (IEQ) factors exist? What kind of exposure-response functions have been defined for them?

Answer

Rationale

Indoor environment quality factors(-)
ObsExposure agentResponseResponse metricExposure routeExposure unitERF parameterERFSignificanceDescription/Reference
1Visible dampness and/or mold or mold odorRespiratory health effectInhalationyes/noORseveral, see Note 1Note 1
2Dampness or mold, minimalMental health problemsPrevalenceyes/noOR1.39 (1.02-1.89)Shenassa et al. 2007
3Dampness or mold, moderateMental health problemsPrevalenceyes/noOR1.44 (1.08-1.92)Shenassa et al. 2007
4Dampness or mold, extensiveMental health problemsPrevalenceyes/noOR1.34 (0.97-1.85)Shenassa et al. 2007
5Dampness and/or moldMental health problemsPrevalenceyes/noOR1.76 (1.17-2.66)0.0056Hopton and Hunt 1996
6Dampness and/or moldSelf-assessed health poorerNote 2
7Living in a low income household Mental health problemsPrevalenceyes/noOR1.61 (1.06-2.44)0.0231Hopton and Hunt 1996
8Respondent unemployedMental health problemsPrevalenceyes/noOR1.55 (0.99-2.42)0.0483Hopton and Hunt 1996
9Living in flat instead of houseMorbidityMorbidityyes/noRR1.57Fanning 1967
10Floor of livingPsychoneurotic disorderIncidence1st vs. groundRR1.06Fanning 1967 (RR calculated from Table 8)
11Floor of livingPsychoneurotic disorderIncidence2nd vs. groundRR1.74Fanning 1967 (RR calculated from Table 8)
12Floor of livingPsychoneurotic disorderIncidence3rd vs. groundRR2.02Fanning 1967 (RR calculated from Table 8)
13Environmental tobacco smokeLung cancerMorbidityInhalationyes/noRR1.21 (1.13-1.30)Note 7
14Environmental tobacco smokeIschaemic heart diseaseMortalityInhalationyes/noRR1.27 (1.19-1.36)Note 7
15Environmental tobacco smokeAsthmaMorbidityInhalationyes/noRR1.97 (1.19-3.25)Age >21; Note 7
16Environmental tobacco smokeAsthmaMorbidityInhalationyes/noRR1.32 (1.24-1.41)Age <14; Note 7
17Environmental tobacco smokeLung infectionsMorbidityInhalationyes/noRR1.55 (1.42-1.69)Age <2; Note 7
18Environmental tobacco smokeMiddle ear inflammationMorbidityInhalationyes/noRR1.38 (1.21-1.56)Age <3; Note 7
19Environmental tobacco smokeIrritation of eyes and mucosa
20Environmental tobacco smokeOdour problemsInhalation
21Environmental tobacco smokeComfort of housing
22Environmental tobacco smokeChronic infectionsInhalation
23Wood smokeRespiratory health effectInhalationNote 3, Note 4
24Wood smokeIrritation of eyes and mucosa
25Wood smokeRespiratory health effectInhalation
26Wood smokeOdour problemsInhalation
27Wood smokeComfort of housing
28Wood smokeChronic infectionsInhalation
29Wood smokeCancerInhalation
30VOCsIrritation symptoms
31CO2HeadacheInhalation
32CO2TirednessInhalation
33COHeadacheInhalation
34COTirednessInhalation
35Insufficient air exchangeHeadache
36Insufficient air exchangeTiredness
37Insufficient air exchangeDecreased ability to concentrate
38Insufficient air exchangeFeeling of fug
39Thermal conditions; heatTiredness
40Thermal conditions; heatDecreased ability to concentrate
41Thermal conditions; heatIncreased respiratory symptoms
42Thermal conditions; heatFeeling of dryness
43Thermal conditions; heatComfort of housing
44Thermal comfort (draught or cold)Mental health problemsNote 2
45Thermal comfort (heat or cold)DepressionNote 2
46Thermal comfort (heat or cold; general perception of thermal problems)Self-assessed health poorerNote 2
47Thermal conditions (cold)Feeling of draught
48Thermal conditions (cold)Comfort of housing
49NoiseHearing injury
50NoiseSleep disturbance
51NoiseStress
52NoiseComfort of housing
53Proximity to trafficMortality
54RadonLung cancerNote 5
55Relative humidity
56PM2.5MortalityNote 3
57PM2.5Chronic bronchitis
58PM2.5Lung cancer
59Reduced space (house/flat)DepressionNote 2
60Reduced space (house/flat)Mental health problemsNote 2
61Reduced space (house/flat)Self-assessed health poorerNote 2
62Access to gardenDepressionNote 2
63Floor levelMental health problemsNote 2
64OvercrowdingMental health problemsNote 2
65OvercrowdingSelf assessed health poorerNote 2
66Sensory IAQVarious health and well-being parameters
67Maternal employmentMaltreatment of childrenPrevalenceno/yesOR2.82 (1.59-5.00)Sidebotham et al. 2002
68No. of house moves in previous 5 yearsMaltreatment of childrenPrevalence2-3 vs. 0-1OR1.32 (0.77-2.27)Sidebotham et al. 2002
69No. of house moves in previous 5 yearsMaltreatment of childrenPrevalence4 or more vs. 0-1OR2.81 (1.59-4.96)Sidebotham et al. 2002
70Overcrowded accomodationMaltreatment of childrenPrevalenceyes/noOR2.16 (1.27-3.70)Sidebotham et al. 2002
71AccomodationMaltreatment of childrenPrevalenceCouncil vs. owned/mortgargedOR7.65 (3.30-17.75)Sidebotham et al. 2002
72AccomodationMaltreatment of childrenPrevalenceRented vs. owned/mortgargedOR4.47 (1.82-10.98)Sidebotham et al. 2002
73Social Network Score < 21Maltreatment of childrenPrevalenceyes/noOR3.09 (1.84-5.19)Sidebotham et al. 2002
74Paternal employementMaltreatment of childrenPrevalenceno/yesOR2.33 (1.43-3.77)Sidebotham et al. 2002
75Car useMaltreatment of childrenPrevalenceno/yesOR2.33 (1.41-3.83)Sidebotham et al. 2002
76No. of deprivation indicatorsMaltreatment of childrenPrevalence1 vs. 0OR9.58 (2.64-34.81)Note 6; Sidebotham et al. 2002
77No. of deprivation indicatorsMaltreatment of childrenPrevalence2 vs. 0OR23.44 (6.61-83.15)Note 6; Sidebotham et al. 2002
78No. of deprivation indicatorsMaltreatment of childrenPrevalence3 vs. 0OR59.30 (17.52-200.76)Note 6; Sidebotham et al. 2002
79No. of deprivation indicatorsMaltreatment of childrenPrevalence4 vs. 0OR111.36 (32.31-383.801)Note 6; Sidebotham et al. 2002
80House dampnessProblems in energy (according Nottingham Health Profile)Prevalenceyes/noOR2.13Packer et al. 1994 (OR calculated from Table 8)
81House dampnessSocial isolation (according Nottingham Health Profile)Prevalenceyes/noOR2.04Packer et al. 1994 (OR calculated from Table 8)
82House dampnessProblems in sleep (according Nottingham Health Profile)Prevalenceyes/noOR1.50Packer et al. 1994 (OR calculated from Table 8)
83House dampnessProblems in emotional reactions (according Nottingham Health Profile)Prevalenceyes/noOR1.27Packer et al. 1994 (OR calculated from Table 8)
84House dampnessProblems in physical mobility (according Nottingham Health Profile)Prevalenceyes/noOR1.37Packer et al. 1994 (OR calculated from Table 8)
85House dampnessPerception of pain (according Nottingham Health Profile)Prevalenceyes/noOR1.28Packer et al. 1994 (OR calculated from Table 8)
86SmokingChronic respiratory diseasePrevalenceInhalationyes/noOR4.36 (2.46-7.74)0.000Blackman et al. 2001
87DampnessChronic respiratory diseasePrevalenceInhalationyes/noOR2.10 (1.36-3.50)0.004Blackman et al. 2001
88Unwaged householdChronic respiratory diseasePrevalenceyes/noOR1.73 (1.24-2.41)0.001Blackman et al. 2001
89Unsafe neighborhoodMental health problemsPrevalenceyes/noOR2.35 (1.41-3.92)0.001Blackman et al. 2001
90DraughtsMental health problemsPrevalenceyes/noOR2.28 (1.41-3.69)0.001Blackman et al. 2001
91RehousingPalpitations/breathlessnessPrevalenceyes/noOR0.71Pettricrew et al. 2009 (OR calculated from Table 5)
92RehousingPersistent coughPrevalenceyes/noOR0.89Pettricrew et al. 2009 (OR calculated from Table 5)
93RehousingPainful jointsPrevalenceyes/noOR0.70Pettricrew et al. 2009 (OR calculated from Table 5)
94RehousingFaints/dizzinessPrevalenceyes/noOR0.68Pettricrew et al. 2009 (OR calculated from Table 5)
95RehousingDifficulty in sleepingPrevalenceyes/noOR0.49Pettricrew et al. 2009 (OR calculated from Table 5)
96RehousingSinus trouble/catarhPrevalenceyes/noOR0.79Pettricrew et al. 2009 (OR calculated from Table 5)
97Housing tenurePoor self-rated healthPrevalencerenter vs. ownerOR1.48 (1.31-1.68)Pollack et al. 2004


Precision and Plausability of Hopton and Hunt (1996)

- Reporting bias: Perhaps ít´s difficult to use subjective data due to reporting bias. This is because people may answer in different ways or they don´t answer at all. In addition, people experience household conditions differently.

- Possible confounding variables such as sociodemographic and economic variables, e.g. age and income, were controlled.

- Selection bias: The sample is clearly not representative of the general population and therefore the analysis focuses on differences within the sample. Thus it´s worth considering if the results can be generalized to whole population.


Precision and Plausability of Sidebotham et al. (2002)

- Maltreatment is defined and measured as registration for physical injury, neglect, sexual abuse, emotional abuse. That way all maltreatments, which are not registered are not taken into account.

- The measurement of the social class is not too accurate, because no allowance for nonworking mothers and no parental social class allocated for single mothers can be applied.

- The nature of relationship with child maltreatment is complex (confounder, cultural values, etc). That causes problems in finding an association or causality between an exposure factor and maltreatment. Moreover, maltreatment has different definition in different cultural groups.

- The parental income is not measured directly, but car ownership as a proxy indicator and the receipt of welfare payment are used.

- Controlling for social factors was done.

- Large amount of prospectively collected data are used in in the study, which is a clear strength.

- The participation is lower among the maltreated group, which might influence the outcome of the statistical analysis or bias the results of the study.

- The risk of social bias and no way of measuring the effect of such bias. A social bias can be defined as a prejudgement of a specific social group. In this case, it might be that those, who collected the data might have expectations, that parents which lower or higher social background are more prone to maltreat their child and let this expectation influence their interpretation of the results. This is not very likely here, though, because all parameters which were used for the analysis can me measured and there is not much freedome for interpretation.


Precision and Plausability of Packer et al. (1994)

- health problems: possibility of headache, mental problems, emotional reactions, social isolation and pain.

- social factors: unemployment, single parent, lone adult and unemployment with sickness or disability

- lifestyle: consumption of alcohol and smoking


Precision and Plausability of Blackman et al. (2001)

- Bias in respondents answers to realistically evaluate their and family members health

- Some housings that where targets on first survey were demolished during second survey.

- No data from comparison neighbourhood without renewal to back up observed health changes after renewal program.

- Relationship between dampness, draughts and mental health is uncertain, because the mechanism is unknown

- Multivariate analysis using regression model was used to control variables, such as economic, housing, respiratory and mental health related to increase plausability which increases the plausibility of ERF.


Precision and Plausability of D. Fanning (1967)

- The study is quite old. Probably today many other parameters in addition to those used in the article would be measured when conducting this kind of study.

- The study has considered the difference between children and adults.

- The study has not considered the differences between different flats and houses. They have only categories for houses and flats but the differences between houses are not considered. This may cause bias to the study.


Precision and Plausability of Petticrew et al. (2009)

- Data collection at the three occassions in the intervention group before moving, one year after moving and 2 years after moving to the social housing gives strenght to the study in analysing changes in the housing circumstances and in neighbourhood.

- Recruitment into the study was discussed by the landlord to the tenant once they have accepted the housing offer which dosn't gives the RSL direct contact with the participant though this serves as a way of good recruitments but it dose not guarantee the authenticity of the data collected. e.g RSL couldn't supply the number of people who refuse to participate in the study to the SHARP research team.

- Broad range of adult household categories in the intervention group which was used as a base for recruiting the comparism group stenghthen the study. (family households, with children under age of sixteen years, older households where the respondents and adult members of the households were of pensionable age, and adult households with a combination of relationships, including parents with children atleast 16 years of age, people unrelated to one and another and couples )

- Qualitative and quantitative findings were only presented for 1 year(wave 2) in the study which dose not proof if the effects are sustained and probabely if differences in health outcomes occur at two years in the intervention and comparism groups.

- recollection bias may occur during interview if participant in the groups if they can not recall adequately past occurences relating to health, housing and neighbourhood questions after one year and two years of movement to the new house.

- Bias in subsequent analysis can also occur if there is any significant changes in the groups associated with self reported health.


Precision and Plausibility of Pollack et al. (2004)

The study controls some factors which can potentially cause bias in the result, like socioeconomic factors, relation to the neighbours and pollution of the local environment. However, the potential effects of working conditions on the health of the study subjects has not been addressed. In addition, it should be found out whether life style, diet, smoking, and use of alcohol are included it in socioeconomic factors.

Indoor environment quality (IEQ) factors

IEQ factors(h-1,%,%,%,-,%,%,%,Bq/m3)
ObsBuildingHeatingVentilation rateDampness%Smoking%Biomass burning%Indoor background emissionsIn noise areas%Too hot in summer%Too cold in winter%RadonDescription
1Detached housesDistrict0.71 (0.3-1.12)5-16.52.35 (1.4-3.4)15100 (95-105)Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
2Detached housesElectricity0.71 (0.3-1.12)5-16.52.35 (1.4-3.4)15100 (95-105)Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
3Detached housesOil0.71 (0.3-1.12)5-16.52.35 (1.4-3.4)15100 (95-105)Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
4Detached housesWood0.71 (0.3-1.12)5-16.52.35 (1.4-3.4)15100 (95-105)Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
5Detached housesGeothermal0.71 (0.3-1.12)5-16.52.35 (1.4-3.4)15100 (95-105)Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
6Row housesDistrict0.71 (0.3-1.12)5-16.52.35 (1.4-3.4)21100 (95-105)Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
7Apartment housesDistrict0.71 (0.3-1.12)5-16.52.35 (1.4-3.4)30100 (95-105)Gens, 2012; Turunen et al. 2010; Haverinen-Shaughnessy, 2012; Assumption based on city´s data; Kurttio 2006
8Leisure housesElectricity
9OfficesDistrict0Assumption
10CommercialDistrict0Assumption
11Health and social sectorDistrict0Assumption
12PublicDistrict0Assumption
13SportsDistrict0Assumption
14EducationalDistrict240Haverinen-Shaughnessy et al. 2012; Assumption
15IndustrialDistrict0Assumption
16OtherDistrict

Gens 2012 [1]

Haverinen-Shaughnessy 2010 [2]

Haverinen-Shaughnessy et al. 2012 [3]

Turunen et al. 2010 [4]


See also

Urgenche research project 2011 - 2014: city-level climate change mitigation
Urgenche pages

Urgenche main page · Category:Urgenche · Urgenche project page (password-protected)

Relevant data
Building stock data in Urgenche‎ · Building regulations in Finland · Concentration-response to PM2.5 · Emission factors for burning processes · ERF of indoor dampness on respiratory health effects · ERF of several environmental pollutions · General criteria for land use · Indoor environment quality (IEQ) factors · Intake fractions of PM · Land use in Urgenche · Land use and boundary in Urgenche · Energy use of buildings

Relevant methods
Building model · Energy balance · Health impact assessment · Opasnet map · Help:Drawing graphs · OpasnetUtils‎ · Recommended R functions‎ · Using summary tables‎

City Kuopio
Climate change policies and health in Kuopio (assessment) · Climate change policies in Kuopio (plausible city-level climate policies) · Health impacts of energy consumption in Kuopio · Building stock in Kuopio · Cost curves for energy (prioritization of options) · Energy balance in Kuopio (energy data) · Energy consumption and GHG emissions in Kuopio by sector · Energy consumption classes (categorisation) · Energy consumption of heating of buildings in Kuopio · Energy transformations (energy production and use processes) · Fuels used by Haapaniemi energy plant · Greenhouse gas emissions in Kuopio · Haapaniemi energy plant in Kuopio · Land use in Kuopio · Building data availability in Kuopio · Password-protected pages: File:Heat use in Kuopio.csv · Kuopio housing

City Basel
Buildings in Basel (password-protected)

Energy balances
Energy balance in Basel · Energy balance in Kuopio · Energy balance in Stuttgart · Energy balance in Suzhou


http://en.opasnet.org/en-opwiki/index.php?title=Indoor_environment_quality_(IEQ)_factors&oldid=29149

Keywords

References

  1. Gens 2012 [1]
  2. Haverinen-Shaughnessy 2010 [2]
  3. Haverinen-Shaughnessy et al. 2012 [3]
  4. Turunen et al. 2010 [4]

Related files

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Indoor environment quality (IEQ) factors. Opasnet . [5]. Accessed 25 Nov 2024.