ライフサイエンスコーパス: bedroom

1 nd fast food, and having a television in the bedroom).

2 ranged from 0.17 mSv (kitchen) to 0.58 mSv (bedroom).

3 trol the interior thermal environment in the bedroom.

4 128]), and more specifically in the child's bedroom.

5 were collected in the living room and in the bedroom.

6 monly detected in living room and children's bedroom.

7 266 (64%) had a television/computer in their bedroom.

8 (no vs yes) of a television/computer in the bedroom.

9 ause of the privacy and security of upstairs bedrooms.

10 as quantified in dust from pregnant mothers' bedrooms.

11 all collectors (EDCs) from the participants' bedrooms.

12 bient light measured every 30 seconds in her bedroom, 2) personal magnetic field measured at 30-secon

13 Among the children's bedrooms, 50.2 percent had high levels of cockroach alle

14 exchange rate between his breathing zone and bedroom air (lambda(BZ)).

15 of 499 at-risk infants, culturable fungi in bedroom air and dust and outdoor air were measured at th

16 2-3 months, we measured culturable fungi in bedroom air and dust, and in outdoor air.

17 measured in matching samples of residential bedroom air collected by passive sampler and in sieved v

18 cupant-associated emission factors affecting bedroom air composition in addition to direct emissions

19 Cs) to examine concentration enhancements in bedroom air during sleep and to calculate VOC emission r

20 ifically characterize the composition of the bedroom air that they experience during sleep.

21 Despite highly variable exposures, bedroom allergen burden is strongly associated with the

22 Bedroom allergen exposures contribute to allergic diseas

23 ional, and climatic factors, associated with bedroom allergen exposures in a nationally representativ

24 s ratio was 1.13 (95% CI: 0.88, 1.44) in the bedroom and 1.08 (95% CI: 0.85, 1.38) in the most lived-

25 confidence interval (CI): 0.69, 1.37) in the bedroom and 1.09 (95% CI: 0.78, 1.51) in the most lived-

26 dex equaled the mean number of residents per bedroom and bathroom.

27 magnetic fields for 24 hours in the child's bedroom and for 30 seconds in three or four other rooms

28 were more frequently detected in homes with bedroom and kitchen on the same floor as compared with d

29 House dust PAH loadings in the bedroom and living room in the same home were significan

30 icant reductions in Der p1 concentrations in bedroom and living-room carpets and the differences betw

31 sampled monthly from the mattress covers and bedroom and living-room carpets.

32 ed over a 1-week period in the participant's bedroom and main living area at baseline, 3 months, and

33 tdoors only and (2) air exchange between the bedroom and other indoor spaces only (as represented by

34 ing conditions: (1) air exchange between the bedroom and outdoors only and (2) air exchange between t

35 Air change rates for the bedroom and, correspondingly, emission rates of sleeping

36 bout one-third of their time asleep in their bedrooms and are themselves emission sources of volatile

37 3.3 microg/m(3) and 10.8 +/- 10.6 ppb in the bedroom, and 12.2 +/- 12.2 microg/m(3) and 12.2 +/- 11.8

38 ors were placed in the kitchen, living room, bedroom, and bathroom.

39 ected serum, dust (office, main living area, bedroom, and vehicle), and handwipe samples from 31 part

40 h dwelling size and proximity of kitchen and bedroom as the most important determinants.

41 Report of having a television in the bedroom at baseline.

42 was often a private act, which took place in bedrooms, bathrooms and toilets, and during the evening

43 ed throughout homes, in some cases elevating bedroom benzene concentrations above chronic health benc

44 iance with initial mattress dust weights and bedroom carpet Der p1 load as covariates.

45 nd pillow covers, and cat exclusion from the bedroom did reduce airborne cat-allergen levels, no effe

46 of nearly 100 VOCs and other species in the bedroom during sleeping periods as compared to the level

47 Dust samples were collected from bedrooms during early life and analyzed for Dermatophago

48 siblings, parental smoking, parental asthma, bedroom dust mite allergen levels at 2 years, and curren

49 Vacuumed bedroom dust samples from the homes of 879 participants

50 o exposed to high levels of that allergen in bedroom dust.

51 aterials (bamboo, shade net, or timber) with bedrooms elevated from the ground and with screened wind

52 rials have investigated the effectiveness of bedroom environmental control programmes involving the u

53 mite allergen in doses comparable to natural bedroom exposure is sufficient to adversely affect pulmo

54 bed (P=0.007), and cockroach allergen on the bedroom floor (P<0.001).

55 f1) allergen in the bed (P<0.001) and on the bedroom floor (P=0.004), D. pteronyssinus in the bed (P=

56 rsibility when exposure was defined by using bedroom floor allergen levels.

57 These relationships were strongest for bedroom floor and bedding dust and were observed in adul

58 Elevated levels of yeasts in bedroom floor dust were associated with reduced: i) whee

59 Modeling the joint effect of bedding and bedroom floor endotoxin on recent asthma symptoms yielde

60 % were cockroach sensitized/exposed based on bedroom floor exposure data.

61 Airborne and bedroom floor mouse allergen concentrations were associa

62 rformed at baseline and 6 and 12 months, and bedroom floor mouse allergen levels were measured every

63 l 1.07-1.41, P = .003 per 2-fold increase in bedroom floor mouse allergen).

64 um sampled to generate composite bedding and bedroom floor samples.

65 Dust from bedding and bedroom floor was analyzed for endotoxin content.

66 Der f 1 or Der p 1) > or = 2 microg/g on the bedroom floor was highest in houses, but 16% of apartmen

67 ergen and dust-mite allergen (Der f1) on the bedroom floor were significantly correlated with reduced

68 dotoxin in settled dust from the baby's bed, bedroom floor, family room, and kitchen floor within the

69 t was collected from the children's beds and bedroom floors and analyzed for mouse (Mus m 1), dust mi

70 that from smooth floors, dust from carpeted bedroom floors had 2.1 times the risk of dust mite aller

71 n concentrations were as follows (in EU/mg): bedroom floors, 35.3 (5th-95th percentile, 5.0-260); bed

72 ), and BDE-153 (p < 0.039), from the adult's bedroom for BDE-99 (p < 0.019) and from all rooms for BD

73 attainment, household composition, and quiet bedroom for sleep) were evaluated separately, and using

74 adiposity, carpeting or a rug in the child's bedroom, higher maternal education, and higher neighborh

75 reen time or a television or computer in the bedroom in early school age and adverse cognitive, execu

76 ent to estimated daily exposure in a typical bedroom) in three weekly sessions for 4 wk.

77 easures of fungal diversity data in infants' bedrooms, limiting the potential to measure long-term as

78 After adjustment for these factors, higher bedroom magnetic field level was associated with signifi

79 isk did not increase with measured nighttime bedroom magnetic field level, wiring configuration of th

80 to the amount of time children spent in the bedroom, mattress dust may be an important source of exp

81 4-hour measurement obtained in the subject's bedroom, metrics evaluated included measures of central

82 climatic variation) and the micro level (the bedroom milieu and factors that affect it) in order to f

83 rring on the indoor stairs (n = 24, 29%) and bedroom (n = 17, 21%).

84 Increases in bedroom NO(2) concentrations were associated with increa

85 l spore counts per cubic metre of air in the bedroom of the enrolled child, the main living spaces an

86 injuries was higher for fires that began in bedrooms or living areas (relative risk, 3.7); that were

87 cipants either slept all night in laboratory bedrooms or remained awake all night.

88 bathroom is about 5m down the hall from the bedroom") or temporal ("the coffee is ready about 3 min

89 and by measurement of magnetic fields in the bedroom over a 7-day period for 347 cases and 286 contro

90 lected from offices (r = 0.35, p = 0.06) and bedrooms (r = 0.39, p = 0.04), but not with dust from ma

91 m main living areas (r = 0.42, p = 0.02) and bedrooms (r = 0.49, p = 0.008), but not with dust from o

92 stic animals, especially infected dogs, from bedrooms; removing potential refuges for bugs from walls

93 9 h and 33.7 h of PAC use in living room and bedroom, respectively.

94 SARS-CoV-2 was identified in 60 (24%) of 248 bedroom samples, 66 (27%) of 241 communal room samples,

95 safe, and there was no transmission to adult bedroom sharers during the 90-day period.

96 , maternal smoking, having an older sibling, bedroom sharing, and cooking with fuels were explored as

97 s, one cloakroom cold tap, one bath, and one bedroom sink mixer [hot/cold] taps).

98 clothing to active bed bugs moving within a bedroom sized arena and (2) elevation of CO2 to a level

99 No prospective study has assessed whether a bedroom television confers an additional risk for obesit

100 Having a bedroom television is associated with weight gain beyond

101 In multivariate analyses, having a bedroom television was associated with an excess BMI of

102 Bedroom televisions were reported by 59.1%of participant

103 With the high prevalence of bedroom televisions, the effect attributable to this ris

104 g, it becomes increasingly important to keep bedroom temperature cool in the summer.

105 r of germs that has left him isolated in his bedroom, unable to eat, and wishing he were dead.

106 V time, and removing the TV from the child's bedroom, using (1) motivational coaching at home and by

107 A television/computer in the bedroom was associated with an increase in inhibition (-

108 After a 1 mo baseline period, subjects' bedrooms were equipped with an active or placebo air cle

109 d Rat n 1) in dust vacuumed from nearly 7000 bedrooms were measured by using immunoassays.

110 ty because people spend considerable time in bedrooms, where they come into close contact with allerg

111 th, smear-positive index patient, and shared bedroom with an index patient (P < .001 for each), as we

112 ection, skin test induration >=10 mm, shared bedroom with an index patient, exposure to more than 1 i

113 CrI 0.63-0.94) and were more likely to share bedrooms with strain-colonised individuals (OR 1.33, CrI