Advanced Nutrition Assessment and Monitoring_Final Paper
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Transcript of Advanced Nutrition Assessment and Monitoring_Final Paper
1
Final Report: Analysis of Underweight and Intervention Recommendations
Western Kenya and Nyanza
GCHB 7090
Megan Hall
Abstract
The western region of Kenya experiences high rates of underweight and stunted children; Table
1 shows the prevalence of underweight and stunting by district. Focusing on an aimed 5% rate of
underweight, this report examines the factors associated with underweight, specifically analyzing
the questions: are source of drinking water, toilet facility and roof type associated with
underweight. The dataset used in this analysis is extracted from DHS 1994 results. After cleaning
the dataset, independent variables—including source of drinking water, toilet facility, roof type
(as proxy for SES), place of delivery (as proxy for access to health services), education and
occupation were dichotomized and severity of underweight was compared between categories of
each variable. Linear regression of the independent variables revealed that source of drinking
water shows the most reliable significant effect on underweight, especially among high-educated
households. The effect of toilet facility on underweight is unreliable due to the small sample size
of households with improved (flush or ventilated) toilet facilities. The effect of SES on
underweight is confounded by source of drinking water, education and access to health services.
Agriculture and unskilled occupations are associated with underweight, however this effect is
accounted for by education, source of drinking water and SES. To reduce underweight among
children under five years old in western Kenya and Nyanza, nutrition interventions must target
households in South Nyanza—which show the greatest prevalence of underweight—and focus
on improving source of drinking water, taking into account the behavioral differences between
high- and low-educated households that lead to the differential effect of improved source of
drinking water on underweight severity among these households.
Introduction
In western Kenya and Nyanza, 22.1% of people reside in Kisii or Nyamira (n = 488); see Table 1
for distribution of households among other districts, as well as distribution of households among
dichotomized independent variables. Respondents in the DHS dataset range from 15 to 49 years
old, with the average age 28 years (n = 2,209) and 72.25% of households include a children
under five years old. The severity of underweight ranges from -5.29 to 3.72 z-score, with a mean
of -0.9524 (n = 1,023). Stunting ranges from -6.00 to 5.41 z-score, with a mean of -1.281(n =
1,023). Using a cut-off of -2.00 z-score for underweight and stunting, the prevalence of
underweight and stunting in western Kenya and Nyanza is 20.6% (n = 211) and 30.4% (n = 311),
respectively. Table 1 shows the prevalence of underweight and stunting in each district, as well
as the independent variables under analysis in this report.
Targeting Priorities
As see in Table 1, South Nyanza has the highest prevalence of underweight (35%, n = 130) and
stunting (42%, n = 130) and is the only district with these prevalences substantially greater than
the national averages of 21% and 30%, respectively. With 130 households of the total 1,023 in
the sample dataset, South Nyanza comprises 12.7% of the population of western Kenya. For
these reasons, households experiencing underweight in South Nyanza are the target priority for
this analysis.
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Results
Source of Drinking Water
Surface water as source of drinking water is significantly associated with a greater prevalence of
underweight (24%, n = 564), compared to well or piped water (17%, n = 454); this difference has
p = 0.009, as seen in Table 1, and shows an effect size of -0.244 (n = 1,017, p = 0.004), as seen
in Table 2. This effect size predicts a 7.8 percentage point increase in underweight prevalence.
Linear regression of source of drinking water revealed a significant interaction with toilet facility
(p = 0.041, n = 1,015) as well as with education (p = 0.034, n = 1,017), but no interaction with
access to health services, as seen in Table 2. Table 3 shows the two-by-two analysis of the
interaction between source of drinking water and toilet facility; because there are so few
households that report having a flush or ventilated toilet, this interaction is not reliable for
planning a nutrition intervention.
The two-by-two analysis between source of drinking water and education, found in Table 4,
revealed a significant difference in the severity of underweight between high-educated (z = -
0.4940, n = 124) and low-educated (z = -0.9417, n = 330) households using well or piped
drinking water, with p = 0.001. Additionally, there was a significant difference in the severity of
underweight between well or piped drinking water (z = -0.4940, n = 124) and surface drinking
water (z = -1.0370, n = 116) among high-educated households, with p = 0.001. Chart 1 illustrates
that underweight improves among households with well or piped drinking water compared to
those utilizing surface water, but this improvement is only significant when those households are
high-educated.
Table 5 shows the linear regression of source of drinking water, access to health services and
SES. The effect of source of drinking water on the severity of underweight remains significant
after controlling for these factors, diminishing from -0.244 (n = 1,017, p = 0.004) to -0.207 (n =
1,003, p = 0.013), indicating that access to health services and SES do not confound the effect of
source of drinking water on underweight.
Toilet Facility
Traditional pit latrine as toilet facility is significantly associated with a greater prevalence of
underweight (22%, n = 926), compared to flush or ventilated toilet facility (11%, n = 91); this
difference has p = 0.017, as seen in Table 1, and shows an effect size of -0.493 (n = 1,017, p =
0.001), as seen in Table 2. This effect size predicts a 15.8 percentage point increase in
underweight prevalence. Linear regression of toilet facility showed no significant interactions
between toilet facility and SES, education or access to health services, as seen in Table 6. Table
7 shows that, after controlling for SES, education and access to health services, the effect of
toilet facility on underweight is no longer significant, diminishing from -0.493 (p = 0.001, n =
1,017) to -0.227 (p = 0.158, n = 1,003), indicating that these factors confound the effect of toilet
facility on underweight.
Roof Type as Proxy for SES
Grass or thatch roof is significantly associated with a greater prevalence of underweight (23%, n
= 563), compared to corrugated iron roof (18%, n = 443); this difference has p = 0.035, as seen
in Table 1, and shows an effect size of -0.257 (n = 1,005, p = 0.004), as seen in Table 8. This
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effect size predicts an 8.2 percentage point increase in underweight prevalence. Linear regression
of roof type, as seen in Table 8, showed no significant interactions between roof type and source
of drinking water, education or place of delivery. After controlling for source of drinking water,
education and place of delivery, the effect of roof type on the severity of underweight decreased
slightly to -0.204, but remained significant (p = 0.018, n = 1,004), indicating that source of
drinking water, education and place of delivery do not confound the effect of roof type on
underweight. The -0.204 effect size of roof type on underweight predicts a 6.5 percentage point
increase in underweight prevalence.
Agriculture and Skilled Occupations
As seen in Table 1, Agriculture and skilled occupations are associated with a greater prevalence
of underweight (23%, n = 487) compared to professional, sales, domestic and unskilled
occupations (20%, n = 333) and clerical and services occupations (18%, n = 109), however these
differences are not significant. As seen in Table 10, linear regression of agriculture and skilled
occupations revealed that the effect of agriculture and skilled occupations on the severity of
underweight is confounded by education, water source and roof type, indicating that these
factors—education, source of drinking water and SES—account for the effect of occupation on
underweight status.
Discussion and Conclusions
This analysis found that a nutrition intervention in the Western Kenya and Nyanza region must
target South Nyanza district, as this district has the highest prevalence of underweight children.
An intervention in this region must focus on source of drinking water as the primary intervention
variable, with SES as a secondary intervention variable. Toilet facility is not a reliable
intervention variable as the sample of households with improved toilet facilities was not large
enough in this dataset to conclude that the observed effect of toilet facility on underweight was a
real effect. Agriculture and skilled occupations are associated with underweight, but this
association is explained by the tendency of these households to have low education, low SES and
surface drinking water.
Source of drinking water had the most reliable effect on the severity of underweight in Western
Kenya and Nyanza, but this effect was modified by the education level of the household so that
improved source of drinking water (well or piped water) was significantly associated with an
improvement in underweight only among high-educated households. Interventions aimed at
reducing the severity and prevalence of underweight in Western Kenya and Nyanza must
prioritize improving source of drinking water, but take into consideration the behavioral
differences between high- and low-educated households. Formative research is needed to
develop an understanding of these behavioral differences in order to contextualize nutrition
interventions, as well as to develop an appropriate educational piece of the intervention in order
to ensure that improving households’ source of drinking water leads to the anticipated
improvement in underweight. Additionally, source of drinking water was associated with
improvement in underweight regardless of access to health services and SES, indicating that
improvement in source of drinking water will predict an improvement in underweight across all
income levels and throughout rural regions that may have limited health facilities. SES must be a
secondary intervention variable because improvement in SES is associated with an improvement
in underweight regardless of source of drinking water, education or access to health services.
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Tables and Charts
Table 1. Distribution of population among independent variables and prevalence of underweight
and stunting by district, water source, toilet facility, SES, access to health services,
education and occupation.
Table 2. Linear regression of underweight by source of drinking water (badwater) and
interactions with toilet facility (badtoilet), education (lowed) and access to health services
(ddelpl): B Coefficient (t, p).
Table 3. Mean underweight z-score by source of drinking water and toilet facility (n).
Table 4. Mean underweight z-score by source of drinking water and education (n).
Chart 1. Interaction between source of drinking water and level of education.
Table 5. Linear regression of underweight by source of drinking water (badwater), access to
health services (ddelpl) and SES (badroof): B Coefficient (t, p).
Table 6. Linear regression of underweight by toilet facility (badtoilet) and interactions with SES
(badroof), education (lowed) and access to health services (ddelpl): B Coefficient (t, p).
Table 7. Linear regression of underweight by toilet facility (badtoilet), SES (badroof), education
(lowed) and access to health services (ddelpl): B Coefficient (t, p).
Table 8. Linear regression of underweight by SES (badroof) and interactions with source of
drinking water (badwater), education (lowed) and access to health services (ddelpl): B
Coefficient (t, p).
Table 9. Linear regression of underweight by SES (badroof), source of drinking water
(badwater), education (lowed) and access to health services (ddelp): B Coefficient (t, p).
Table 10. Linear regression of underweight by agriculture occupation (dag), education (lowed),
source of drinking water (badwater) and SES (badroof): B Coefficient (t, p).
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Table 1. Distribution of population among independent variables and prevalence of
underweight and stunting by district, source of drinking water, toilet facility, SES, access to
health services, education and occupation.
Underweight
(<= -2SD)
Stunting
(<= -2SD)
n % n % n %
District 2,209 1023 21 1023 30
S. Nyanza – rural 257 11.6 130 35 130 42
Kisii/Nyamira – rural 488 22.1 195 21 195 28
Bungoma – rural 396 17.9 215 21 215 36
Siaya – rural 408 18.51 182 20 182 34
Kakamega - rural 381 17.2 182 16 182 25
Other rural 161 7.3 69 9 69 12
Other urban 118 5.3 50 14 50 20
Source of drinking water (badwater) 2,195 1018 1018
Well, piped 955 43.5 454 17* 545 26*
Surface water 1,240 46.5 564 24 564 34
Toilet facility (badtoilet) 2,192 1017 1017
Flush, ventilated 209 9.5 91 11* 91 15*
Traditional, bush 1,983 90.5 926 22 926 32
SES (badroof) 2,152 1006 1006
Corrugated iron 1,082 50.3 443 18* 443 26*
Grass, thatch 1,070 49.7 563 23 563 34
Access to health services (ddelpl) 1,214 1022 1022
Government, private 426 35.1 370 16* 370 28
Home 788 64.9 652 23 652 31
Education (lowed) 2,209 1023 1023
Secondary+ 472 21.4 241 17 241 23*
None, primary 1,737 78.6 782 22 782 30
Occupation (partocc) 1,565 929 929
Agriculture, skilled 833 53.2 487 23 487 34
Professional, sales, domestic, unskilled 539 34.4 333 20 333 31
Clerical, services 193 12.3 109 18 109 21
* Denotes p-value < 0.05
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Table 2. Linear regression of underweight by source of drinking water (badwater) and
interactions with toilet facility (badtoilet), education (lowed) and access to health services
(ddelpl): B Coefficient (t, p).
Variable Model 1 Model 2 Model 3 Model 4
badwater -0.244
(-2.920, 0.004)
0.443
(1.373, 0.170)
-0.543
(-3.189, 0.001)
-0.301
(-2.183, 0.029)
badtoilet -- -0.247
(-1.430, 0.153)
-- --
badwater*badtoilet -- -0.685
(-2.048, 0.041)
-- --
lowed -- -- -0.448
(-3.224, 0.001)
--
badwater*lowed -- -- 0.415
(02.124, 0.034)
--
ddelpl -- -- -- -0.366
(-2.859, 0.004)
badwater*ddelpl -- -- 0.101
(0.583, 0.560)
Constant -0.819 -0.201 -0.494 -0.589
Adj R sq 0.008 0.024 0.018 0.018
N 1017 1015 1017 1016
Table 3. Mean underweight z-score by source of drinking water and toilet facility (n).
Source of drinking water
Toilet
facility
Well, piped Surface TOTAL p
Flush -0.6109 (69) -0.1677 (22) -0.5037 (91) 0.215
Bush -0.8574 (384) -1.099 (541) -0.9990 (925) 0.006
TOTAL -0.8199 (453) -1.063 (563) -0.9456 (1016) .004
p 0.143 0.002 0.001
Table 4. Mean underweight z-score by source of drinking water and education (n).
Source of drinking water
Education
Well, piped Surface TOTAL p
High -0.4940 (124) -1.0370 (116) -0.7564 (240) 0.001
Low -0.9417 (330) -1.0699 (448) -1.0135 (782) 0.182
TOTAL -0.8194 (454) -1.0631 (564) -0.9524 (1023) 0.004
p 0.001 0.816 0.008
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Table 5. Linear regression of underweight by source of drinking water (badwater), access
to health services (ddelpl) and SES (badroof): B Coefficient (t, p).
Variable Model 1 Model 2 Model 3
badwater -0.244
(-2.920, 0.004)
-0.237
(-2.853, 0.004)
-0.207
(-2.483, 0.013)
ddelpl -- -0.311
(-3.614, 0.000)
-0.235
(-2.675, 0.008)
badroof -- -- -0.214
(-2.524, 0.012)
Constant -0.819 -0.624 -0.579
Adj R sq 0.008 0.019 0.020
N 1017 1016 1003
-1.2
-1
-0.8
-0.6
-0.4
-0.2
0
Well Surface
Chart 1. Interaction between source of drinking water and level of education.
High Low
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Table 6. Linear regression of underweight by toilet facility (badtoilet) and interactions with
SES (badroof), education (lowed) and access to health services (ddelpl): B Coefficient (t, p).
Variable Model 1 Model 3 Model 2 Model 4
badtoilet -0.493
(-3.391, 0.001)
-0.423
(-2.423, 0.016)
-0.619
(-2.988, 0.003)
-0.533
(-2.865, 0.004)
badroof -- -0.932
(-2.260, 0.024)
-- --
badtoilet*badroof -- 0.745
(1.766, 0.078)
-- --
lowed -- -- -0.541
(-1.934, 0.053)
--
badtoilet*lowed -- -- 0.408
(1.359, 0.174)
--
ddelpl -- -- -- -0.583
(-1.998, 0.046)
badtoilet*ddelpl -- -- -- 0.348
(1.137, 0.256)
Constant -0.504 -0.463 -0.272 -0.305
Adj R sq 0.010 0.016 0.016 0.018
N 1017 1005 1017 1015
Table 7. Linear regression of underweight by toilet facility (badtoilet), SES (badroof),
education (lowed) and access to health services (ddelpl): B Coefficient (t, p).
Variable Model 1 Model 2 Model 3 Model 4
badtoilet -0.493
(-3.630, 0.001)
-0.295
(-1.857, 0.064)
-0.265
(-1.645, 0.100)
-0.228
(-1.412, 0.158)
badroof -- -0.220
(-2.549, 0.011)
-0.202
(-2.311, 0.021)
-0.182
(-2.077, 0.038)
lowed -- -- -0.127
(-1.239, 0.216)
-0.072
(-0.684, 0.494)
ddelpl -- -- -- -0.201
(-2.199, 0.028)
Constant -0.504 -0.571 -0.511 -0.458
Adj R sq 0.010 0.011 0.014 0.019
N 1017 1005 1005 1003
9
Table 8. Linear regression of underweight by SES (badroof) and interactions with source of
drinking water (badwater), education (lowed) and access to health services (ddelpl): B
Coefficient (t, p).
Variable Model 1 Model 2 Model 3 Model 4
badroof -0.257
(-3.072, 0.002)
-0.381
(-3.036, 0.002)
-0.278
(-1.543, 0.123)
-0.273
(-1.941, 0.053)
badwater -- -0.335
(-2.677, 0.008)
-- --
badroof*badwater -- 0.228
(1.356, 0.175)
-- --
lowed -- -- -0.179
(-1.334, 0.183)
--
badroof*lowed -- -- 0.061
(0.229, 0.765)
--
ddelpl -- -- -- -0.276
(-2.200, 0.028)
badroof*ddelpl -- -- -- 0.086
(0.489, 0.625)
Constant -0.822 -0.701 -0.701 -0.669
Adj R sq 0.009 0.012 0.012 0.017
N 1005 1005 1005 1004
Table 9. Linear regression of underweight by SES (badroof), source of drinking water
(badwater), education (lowed) and access to health services (ddelpl): B Coefficient (t, p).
Variable Model 1 Model 2 Model 3 Model 4
badroof -0.257
(-3.072, 0.002)
-0.254
(-3.038, 0.002)
-0.230
(-2.694, 0.007)
-0.204
(-2.370, 0.018)
badwater -- -0.209
(-2.498, 0.013)
-0.203
(-2.425, 0.015)
-0.204
(-2.441, 0.015)
lowed -- -- -0.142
(-1.402, 0.161)
-0.078
(-0.753, 0.452)
ddelpl -- -- -- -0.218
(-2.407, 0.016)
Constant -0.822 -0.709 -0.616 -0.537
Adj R sq 0.008 0.014 0.015 0.019
N 1006 1005 1005 1004
10
Table 10. Linear regression of underweight by agriculture occupation (dag), education
(lowed), source of drinking water (badwater) and SES (badroof): B Coefficient (t, p).
Variable Model 1 Model 2 Model 3 Model 4
dag -0.208
(-2.408, 0.016)
-0.186
(-2.138, 0.033)
-0.164
(-1.876, 0.061)
-0.135
(-1.535, 0.500)
lowed -- -0.199
(-1.920, 0.055)
-0.163
(-1.755, 0.800)
-0.072
(-0.675, 0.500)
badwater -- -- -0.201
(-2.303, 0.022)
-0.174
(-1.996, 0.046)
badroof -- -- -- -0.270
(-3.028, 0.003)
Constant -0.866 -0.724 -0.640 -0.613
Adj R sq 0.005 0.008 0.013 0.017
N 929 929 924 911